[go: up one dir, main page]

CN103193324A - Purification method of aquaculture sewage and ecological floating bed based on method - Google Patents

Purification method of aquaculture sewage and ecological floating bed based on method Download PDF

Info

Publication number
CN103193324A
CN103193324A CN2013101385473A CN201310138547A CN103193324A CN 103193324 A CN103193324 A CN 103193324A CN 2013101385473 A CN2013101385473 A CN 2013101385473A CN 201310138547 A CN201310138547 A CN 201310138547A CN 103193324 A CN103193324 A CN 103193324A
Authority
CN
China
Prior art keywords
purification
ecological floating
purification area
floating bed
water
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
CN2013101385473A
Other languages
Chinese (zh)
Other versions
CN103193324B (en
Inventor
顾兆俊
刘兴国
朱浩
时旭
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Fishery Machinery and Instrument Research Institute of CAFS
Original Assignee
Fishery Machinery and Instrument Research Institute of CAFS
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Fishery Machinery and Instrument Research Institute of CAFS filed Critical Fishery Machinery and Instrument Research Institute of CAFS
Priority to CN201310138547.3A priority Critical patent/CN103193324B/en
Publication of CN103193324A publication Critical patent/CN103193324A/en
Application granted granted Critical
Publication of CN103193324B publication Critical patent/CN103193324B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Farming Of Fish And Shellfish (AREA)
  • Biological Treatment Of Waste Water (AREA)

Abstract

本发明涉及一种养殖污水的净化方法,其特征在于:在养殖污水的排水渠道内,沿所述排水渠道依次设置一组生态浮床,所述生态浮床宽度小于所述排水渠道的宽度,深度介于排水渠道水深的90%-100%之间;所述生态浮床包括表层净化区,中层净化区,底层净化区,所述表层净化区和底层净化层的四周用带有过水孔的材料封闭;表层净化区与中层净化区隔开,其内种植挺水植物,并设有生物填料,所述生物填料颗粒的外径大于所述过水孔的内径;中层净化区四周用渔网围住,下方通过渔网与底层净化区隔开,所述中层净化区内养殖滤食性鱼;底层净化区下方封闭,设有陶粒,所述陶粒的外径大于所述过水孔的内径,并以所述陶粒为介质种植沉水植物。

Figure 201310138547

The invention relates to a method for purifying aquaculture sewage, which is characterized in that: in the drainage channel of aquaculture sewage, a group of ecological floating beds are sequentially arranged along the drainage channel, the width of the ecological floating bed is smaller than the width of the drainage channel, and the depth is between Between 90%-100% of the water depth of the drainage channel; the ecological floating bed includes a surface purification area, a middle purification area, and a bottom purification area, and the surroundings of the surface purification area and the bottom purification layer are closed with materials with water holes The surface purification area is separated from the middle purification area, and emergent plants are planted in it, and biological fillers are provided, and the outer diameter of the biological filler particles is greater than the inner diameter of the water hole; the middle purification area is surrounded by fishing nets, The bottom is separated from the bottom purification area by fishing nets, and filter-feeding fish are cultivated in the middle purification area; the bottom bottom purification area is closed and provided with ceramsite, the outer diameter of the ceramsite is greater than the inner diameter of the water hole, and The ceramsite is used as a medium for planting submerged plants.

Figure 201310138547

Description

一种养殖污水的净化方法及基于该方法的生态浮床A purification method for aquaculture sewage and an ecological floating bed based on the method

技术领域technical field

本发明涉及一种养殖污水的净化方法,和基于该方法的生态浮床,属于水产养殖技术领域。The invention relates to a method for purifying aquaculture sewage and an ecological floating bed based on the method, belonging to the technical field of aquaculture.

背景技术Background technique

要保证水产品的质量,必须从生产的源头——养殖水域抓起。随着经济的发展,水域的生态环境受到了严重的破坏,有资料表明,我国现有70%以上的湖泊受到不同程度的污染,约1/3的湖泊富营养化,3000多千米的河段鱼虾基本绝迹。面对渔业生态环境不断恶化的严峻形势,除了环保等部门要加大执法力度,减少各种陆源污染外,海洋与渔业部门应首先采取各种有效措施,最大限度地减少对水产养殖本身造成的污染。To ensure the quality of aquatic products, we must start from the source of production - the breeding waters. With the development of the economy, the ecological environment of the water area has been seriously damaged. According to data, more than 70% of the lakes in our country are polluted to varying degrees, about 1/3 of the lakes are eutrophic, and more than 3,000 kilometers of rivers Segment fish and shrimp are basically extinct. Facing the serious situation of deteriorating fishery ecological environment, in addition to environmental protection and other departments to strengthen law enforcement and reduce various land-based pollution, marine and fishery departments should first take various effective measures to minimize the damage caused to aquaculture itself. pollute.

养殖水域的容量是有限的,由于盲目扩大养殖规模,使得水域的生态平衡遭到破坏,导致产量降低、病害加重、质量下降。The capacity of the breeding waters is limited. Due to the blind expansion of the breeding scale, the ecological balance of the waters is destroyed, resulting in reduced yields, aggravated diseases, and reduced quality.

目前,我国水产养殖场、育苗场的污水基本上是不经处理直接排放的,加之很多地方的养殖场数量多、距离近,场与场之间的进水口、排水口往往近在咫尺,根本不能保证生活、生产用水的质量。At present, the sewage from aquaculture farms and nursery farms in my country is basically discharged directly without treatment. In addition, there are a large number of farms in many places and the distance is close. The water inlets and outlets between farms are often close at hand. The quality of water for living and production cannot be guaranteed.

河道污染部分来自水产养殖污水排放,同时传统水产养殖对水资源消耗颇大,为了治理改善河道的水质,本发明对由水产养殖池塘流入河道的污水排放渠道提出了一种进行净化处理的技术方案。Part of the river pollution comes from aquaculture sewage discharge. At the same time, traditional aquaculture consumes a lot of water resources. In order to control and improve the water quality of the river, the present invention proposes a technical solution for purifying the sewage discharge channel flowing from the aquaculture pond into the river. .

发明内容Contents of the invention

本发明需要解决的技术问题是:水产养殖场、育苗场的污水未经有效的处理,甚至直接排放,加之很多地方的养殖场数量多、距离近,场与场之间的进水口、排水口往往近在咫尺,根本不能保证生活、生产用水的质量;现有的这种养殖方式对水资源的消耗很大,造成了水资源的浪费。The technical problem to be solved in the present invention is: the sewage of aquaculture farms and nursery farms has not been effectively treated, and even directly discharged, in addition, the number of farms in many places is large and the distance is short, and the water inlets and drains between the farms It is often close at hand, and the quality of water for living and production cannot be guaranteed at all; the existing farming method consumes a lot of water resources, resulting in a waste of water resources.

本发明采取以下技术方案:The present invention takes the following technical solutions:

一种养殖污水的净化方法,在养殖污水的排水渠道内,沿所述排水渠道依次设置一组生态浮床,所述生态浮床宽度小于所述排水渠道的宽度,深度介于排水渠道水深的90%-100%之间;所述生态浮床包括表层净化区2,中层净化区5,底层净化区4,所述表层净化区2和底层净化层4的四周用带有过水孔3的材料封闭;表层净化区2与中层净化区5隔开,其内种植挺水植物201,并设有生物填料202,所述生物填料202颗粒的外径大于所述过水孔3的内径;中层净化区5四周用渔网围住,下方通过渔网与底层净化区4隔开,所述中层净化区5内养殖滤食性鱼501;底层净化区4下方封闭,设有陶粒402,所述陶粒402的外径大于所述过水孔3的内径,并以所述陶粒402为介质种植沉水植物401。A method for purifying aquaculture sewage. In the drainage channel of aquaculture sewage, a group of ecological floating beds are sequentially arranged along the drainage channel. The width of the ecological floating bed is smaller than the width of the drainage channel, and the depth is between 90% of the water depth of the drainage channel. Between -100%; Described ecological floating bed comprises surface layer purification area 2, middle layer purification area 5, bottom layer purification area 4, and the surroundings of described surface layer purification area 2 and bottom layer purification layer 4 are sealed with the material that has water hole 3; The surface layer purification zone 2 is separated from the middle layer purification zone 5, in which emergent plants 201 are planted, and a biological filler 202 is provided, and the outer diameter of the biological filler 202 particles is greater than the inner diameter of the water hole 3; the middle layer purification zone 5 Surrounded by fishing nets, the bottom is separated from the bottom purification area 4 by fishing nets, and filter-feeding fish 501 are cultured in the middle purification area 5; The diameter is larger than the inner diameter of the water hole 3, and the submerged plants 401 are planted with the ceramsite 402 as the medium.

每个生态浮床的间隔距离为生态浮床长度的3-5倍。The distance between each ecological floating bed is 3-5 times of the length of the ecological floating bed.

生态浮床宽度为排水渠道水面宽度的2/3。The width of the ecological floating bed is 2/3 of the water surface width of the drainage channel.

所述生态浮床与所述排水渠道岸边固定连接。The ecological floating bed is fixedly connected to the bank of the drainage channel.

所述表层净化区2,中层净化区5,底层净化区4的高度比例约为2:3:1。The height ratio of the surface purification zone 2, the middle purification zone 5, and the bottom purification zone 4 is about 2:3:1.

所述带有过水孔3的材料为亚克力板材。The material with the water hole 3 is an acrylic plate.

所述渔网为聚乙烯网片。The fishing net is polyethylene mesh.

所述滤食性鱼501的密度不超过0.4kg/立方水体。The density of the filter-feeding fish 501 is not more than 0.4kg/cubic water body.

所述生态浮床呈矩形体结构,上部设有浮性框架1,其长宽比为2:1-4:1。The ecological floating bed has a rectangular structure, and a floating frame 1 is arranged on the upper part, and its aspect ratio is 2:1-4:1.

本发明的目的是针对现有技术中的不足,发明应用于标准化水产养殖池塘附属污水排放渠道中的一种净化水质的处理装置及其使用方法。一种箱式生物浮床,可以针对不同水层应用。The purpose of the present invention is to address the deficiencies in the prior art, and to invent a treatment device for purifying water and a method for using it in the subsidiary sewage discharge channels of standardized aquaculture ponds. A box-type biological floating bed can be used for different water layers.

本发明的工作原理:养殖废水经排水渠道排放,流过本发明的生物浮床时,表层净化区2通过其内的生物填料,挺水植物等,可去除养殖废水中的氨氮、磷等负面元素,同时把其转变为生长元素供植物吸收;中层净化区5通过其内的滤食性鱼501,可以过滤悬浮物质,同时,通过从底层向上生长的沉水植物401,能恢复一定量的溶解氧,为了防止滤食性鱼501自身排泄物对水体产生污染,滤食性鱼501的数量不宜太密集,以小于0.4kg/立方米水体为佳;底层净化区4通过设置陶粒402,有助于富营养物质的分解。通过三层不同针对性的净化后,污水可达到环保排放或循环使用的要求。The working principle of the present invention: the aquaculture wastewater is discharged through drainage channels, and when flowing through the biological floating bed of the present invention, the surface layer purification zone 2 passes through the biological fillers, emergent plants, etc. in the aquaculture wastewater, which can remove negative elements such as ammonia nitrogen and phosphorus in the aquaculture wastewater , and transform it into growth elements for plants to absorb; the middle layer purification zone 5 can filter suspended matter through the filter-feeding fish 501 in it, and at the same time, through the submerged plants 401 growing upward from the bottom layer, a certain amount of dissolved oxygen can be recovered , in order to prevent filter-feeding fish 501 self-excretion from polluting the water body, the quantity of filter-feeding fish 501 should not be too dense, preferably less than 0.4kg/m3 water body; Bottom purification zone 4 is provided with ceramsite 402, helps rich Breakdown of nutrients. After three layers of different targeted purification, the sewage can meet the requirements of environmental protection discharge or recycling.

试验结果表明:在排水渠道内放置该生态浮床来净化养殖排放污水,有明显效果。把排水渠道的进口(池塘废水排放出口)和出口设置为采样点,每周对两个点采集一次水样进行水质分析,连续2个月。其中,总氮的去除率平均达到21%;总磷的去除率平均达到8%;氨氮的去除率平均达到17%;亚硝态氮的去除率平均达到11%。The test results show that placing the ecological floating bed in the drainage channel to purify the sewage discharged from aquaculture has obvious effects. Set the inlet of the drainage channel (the outlet of pond wastewater discharge) and the outlet as sampling points, and collect water samples from two points once a week for water quality analysis for 2 consecutive months. Among them, the average removal rate of total nitrogen reaches 21%; the average removal rate of total phosphorus reaches 8%; the average removal rate of ammonia nitrogen reaches 17%; the average removal rate of nitrite nitrogen reaches 11%.

本发明的有益效果在于:The beneficial effects of the present invention are:

1)生态浮床成本低,投入小,养殖废水净化效果明显,性价比很高。1) The cost of the ecological floating bed is low, the investment is small, the purification effect of the breeding wastewater is obvious, and the cost performance is very high.

2)避免养殖废水直接排放,提高了养殖场附近生活,生产用水的质量。2) Avoid the direct discharge of breeding wastewater, and improve the quality of water for living and production near the farm.

3)使得养殖废水能够回收利用,大大节约了水资源。3) It enables the recycling of aquaculture wastewater, which greatly saves water resources.

附图说明Description of drawings

图1是生态浮床的俯视示意图。Figure 1 is a schematic top view of an ecological floating bed.

图2是生态浮床的立面示意图。Figure 2 is a schematic elevation view of the ecological floating bed.

图3是生态浮床的立面剖视示意图。Fig. 3 is a schematic elevation sectional view of the ecological floating bed.

图4是养殖废水排水渠道及其内部设置生态浮床的俯视示意图。Fig. 4 is a schematic top view of the aquaculture wastewater drainage channel and the ecological floating bed inside.

其中,1、浮性框架,2、表层净化区,3、过水孔,4、底层净化区,5、中层净化区,201、挺水植物,202、生物滤料,401、沉水植物,402、陶粒,501、滤食性鱼。Among them, 1. Floating frame, 2. Surface purification area, 3. Water holes, 4. Bottom purification area, 5. Middle purification area, 201. Emerging plants, 202. Biological filter material, 401. Submerged plants, 402, ceramsite, 501, filter-feeding fish.

具体实施方式Detailed ways

下面结合具体实施例对本发明进一步说明。The present invention will be further described below in conjunction with specific examples.

参见图4,在养殖废水的排水渠道内设置一组生态浮床,每个生态浮床的间距为生态浮床长度的3-5倍。生态浮床宽度为排水渠道水面宽度的2/3;浮床深度为排水沟渠内水体深度的90%以上。Referring to Fig. 4, a group of ecological floating beds is set in the drainage channel of the aquaculture wastewater, and the distance between each ecological floating bed is 3-5 times of the length of the ecological floating beds. The width of the ecological floating bed is 2/3 of the width of the water surface of the drainage channel; the depth of the floating bed is more than 90% of the depth of the water body in the drainage ditch.

参见图2,水下部分由三个功能区构成,深度比例约为20cm:60cm:10cm。表层和底层均为一个亚克力箱体,箱体四边钻了若干个过水孔3,保证水流的通畅性;中间四周由聚乙烯网片围成。Referring to Figure 2, the underwater part is composed of three functional areas, and the depth ratio is about 20cm:60cm:10cm. Both the surface layer and the bottom layer are an acrylic box, and several water holes 3 are drilled on the four sides of the box to ensure the unimpeded flow of water; the middle is surrounded by polyethylene mesh.

表层净化区的箱体内放置生物填料202,生物填料202的种类一般选择立体弹性调料,在里面种植一些挺水植物或漂浮性植物均可例如鸢尾、水雍菜、水葫芦等;中层净化区的聚乙烯网里放置一些滤食性鱼类,如白鲢,密度不超于0.4kg/立方水体;底层净化区箱体内放置陶粒作为基质,上面种植沉水性植物,如伊乐藻。Biofiller 202 is placed in the box in the surface purification area. The type of biofiller 202 is generally three-dimensional elastic seasoning, and some emergent plants or floating plants can be planted inside, such as iris, water hyacinth, water hyacinth, etc.; Put some filter-feeding fish in the polyethylene net, such as silver carp, with a density not exceeding 0.4kg/cubic water body; place ceramsite in the bottom purification area box as a substrate, and plant submerged plants on it, such as Elodea.

参见图2-3,表层净化区2水通过过水孔3进入箱体内,经过生物填料201的吸附作用和挺水植物201根系吸收氨氮、磷等,再从过水孔3流出;挺水植物201通过吸收表层水污染元素并转化成其生长元素,可产生额外的美观价值和经济效益,并对区域环境改善有一定的辅助效果。Referring to Fig. 2-3, the water in the surface purification zone 2 enters the box through the water hole 3, absorbs ammonia nitrogen, phosphorus, etc. through the adsorption of the biological filler 201 and the root system of the emergent plant 201, and then flows out from the water hole 3; the emergent plant 201 absorbs surface water pollution elements and converts them into growth elements, which can produce additional aesthetic value and economic benefits, and have a certain auxiliary effect on the improvement of the regional environment.

参见图2-图3,中层净化区5水流经过网片时,网内放养的滤食性鱼可通过其食性调控水中悬浮颗粒及多余浮游生物;Referring to Fig. 2-Fig. 3, when the water flow in the middle purification zone 5 passes through the net, the filter-feeding fish stocked in the net can regulate the suspended particles and excess plankton in the water through their feeding habits;

参见图2-图3,底层净化区4内种植的沉水性植物,茎叶部分在中层净化区5区域内通过光合作用释放氧气,恢复水体中的溶解氧含量。底层净化区4水通过箱体外侧的过水孔3,经过陶粒基质时,可发生硝化反应和反硝化反应,去除氨氮和亚硝态氮,并有助于分解水底层有机营养物的沉积。Referring to Figures 2-3, the stems and leaves of the submerged plants planted in the bottom purification zone 4 release oxygen through photosynthesis in the middle purification zone 5 to restore the dissolved oxygen content in the water. The water in the bottom purification zone 4 passes through the water hole 3 on the outside of the box, and when it passes through the ceramsite matrix, nitrification and denitrification reactions can occur to remove ammonia nitrogen and nitrite nitrogen, and help to decompose the deposition of organic nutrients in the bottom of the water .

试验结果表明:在养殖废水的排水渠道内放置本发明的生态浮床来净化养殖排放污水,有明显效果。把排水渠道的进口(池塘废水排放出口)和出口设置为采样点,每周对两个点采集一次水样进行水质分析,连续2个月。其中,总氮的去除率平均达到21%;总磷的去除率平均达到8%;氨氮的去除率平均达到17%;亚硝态氮的去除率平均达到11%。The test results show that the ecological floating bed of the present invention is placed in the drainage channel of the breeding wastewater to purify the wastewater discharged from the farming, which has obvious effects. Set the inlet of the drainage channel (the outlet of pond wastewater discharge) and the outlet as sampling points, and collect water samples from two points once a week for water quality analysis for 2 consecutive months. Among them, the average removal rate of total nitrogen reaches 21%; the average removal rate of total phosphorus reaches 8%; the average removal rate of ammonia nitrogen reaches 17%; the average removal rate of nitrite nitrogen reaches 11%.

Claims (9)

1.一种养殖污水的净化方法,其特征在于:1. A purification method for aquaculture sewage, characterized in that: 在养殖污水的排水渠道内,沿所述排水渠道依次设置一组生态浮床,所述生态浮床宽度小于所述排水渠道的宽度,深度介于排水渠道水深的90%-100%之间;In the drainage channel of aquaculture sewage, a group of ecological floating beds are arranged sequentially along the drainage channel, the width of the ecological floating bed is smaller than the width of the drainage channel, and the depth is between 90%-100% of the water depth of the drainage channel; 所述生态浮床包括表层净化区(2),中层净化区(5),底层净化区(4),所述表层净化区(2)和底层净化层(4)的四周用带有过水孔(3)的材料封闭;The ecological floating bed includes a surface purification area (2), a middle purification area (5), and a bottom purification area (4). The surface purification area (2) and the bottom purification layer (4) are surrounded by water holes ( 3) material closure; 表层净化区(2)与中层净化区(5)隔开,其内种植挺水植物(201),并设有生物填料(202),所述生物填料(202)颗粒的外径大于所述过水孔(3)的内径;The surface purification area (2) is separated from the middle purification area (5), in which emergent plants (201) are planted, and biological fillers (202) are provided, and the outer diameter of the particles of the biological fillers (202) is larger than that of the filter. inner diameter of the water hole (3); 中层净化区(5)四周用渔网围住,下方通过渔网与底层净化区(4)隔开,所述中层净化区(5)内养殖滤食性鱼(501);The middle purification area (5) is surrounded by fishing nets, and the lower part is separated from the bottom purification area (4) by fishing nets, and filter-feeding fish (501) are cultivated in the middle purification area (5); 底层净化区(4)下方封闭,设有陶粒(402),所述陶粒(402)的外径大于所述过水孔(3)的内径,并以所述陶粒(402)为介质种植沉水植物(401)。The bottom purification area (4) is closed below, with ceramsite (402), the outer diameter of the ceramsite (402) is larger than the inner diameter of the water hole (3), and the ceramsite (402) is used as the medium Plant submerged plants (401). 2.如权利要求1所述的养殖污水的净化方法,其特征在于:每个生态浮床的间隔距离为生态浮床长度的3-5倍。2. The purification method of aquaculture sewage as claimed in claim 1, characterized in that: the distance between each ecological floating bed is 3-5 times of the length of the ecological floating bed. 3.如权利要求1所述的养殖污水的净化方法,其特征在于:生态浮床宽度为排水渠道水面宽度的2/3。3. The purification method of aquaculture sewage as claimed in claim 1, characterized in that: the width of the ecological floating bed is 2/3 of the water surface width of the drainage channel. 4.如权利要求1所述的养殖污水的净化方法,其特征在于:所述生态浮床与所述排水渠道岸边固定连接。4. The purification method of aquaculture sewage according to claim 1, characterized in that: the ecological floating bed is fixedly connected to the bank of the drainage channel. 5.如权利要求1所述的养殖污水的净化方法,其特征在于:所述表层净化区(2),中层净化区(5),底层净化区(4)的高度比例约为2:3:1。5. The purification method of aquaculture sewage as claimed in claim 1, characterized in that: the surface purification zone (2), the middle purification zone (5), and the height ratio of the bottom purification zone (4) are about 2:3: 1. 6.如权利要求1所述的养殖污水的净化方法,其特征在于:所述带有过水孔(3)的材料为亚克力板材。6. The method for purifying aquaculture sewage according to claim 1, characterized in that: the material with the water holes (3) is an acrylic plate. 7.如权利要求1所述的养殖污水的净化方法,其特征在于:所述渔网为聚乙烯网片。7. The purification method of aquaculture sewage as claimed in claim 1, characterized in that: said fishing net is a polyethylene mesh. 8.如权利要求1所述的养殖污水的净化方法,其特征在于:所述滤食性鱼(501)的密度不超过0.4kg/立方水体。8. The method for purifying aquaculture sewage according to claim 1, characterized in that: the density of the filter-feeding fish (501) does not exceed 0.4kg/cubic water body. 9.一种基于权利要求1所述的净化方法的生态浮床,其特征在于:所述生态浮床呈矩形体结构,上部设有浮性框架(1),其长宽比为2:1-4:1。9. An ecological floating bed based on the purification method according to claim 1, characterized in that: the ecological floating bed has a rectangular structure, and the upper part is provided with a floating frame (1), and its aspect ratio is 2:1-4 :1.
CN201310138547.3A 2013-04-19 2013-04-19 A purification method for aquaculture sewage and an ecological floating bed based on the method Expired - Fee Related CN103193324B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201310138547.3A CN103193324B (en) 2013-04-19 2013-04-19 A purification method for aquaculture sewage and an ecological floating bed based on the method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201310138547.3A CN103193324B (en) 2013-04-19 2013-04-19 A purification method for aquaculture sewage and an ecological floating bed based on the method

Publications (2)

Publication Number Publication Date
CN103193324A true CN103193324A (en) 2013-07-10
CN103193324B CN103193324B (en) 2014-07-02

Family

ID=48716170

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201310138547.3A Expired - Fee Related CN103193324B (en) 2013-04-19 2013-04-19 A purification method for aquaculture sewage and an ecological floating bed based on the method

Country Status (1)

Country Link
CN (1) CN103193324B (en)

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103351086A (en) * 2013-07-30 2013-10-16 中国水产科学研究院渔业机械仪器研究所 Ecological treatment circulatory system for discharge water of sea farming pond
CN104003523A (en) * 2014-05-14 2014-08-27 广州中国科学院先进技术研究所 Ecological net cage-based water purification method
CN105906066A (en) * 2016-06-17 2016-08-31 同济大学 Modularized artificial floating island for multi-medium reinforced repair of polluted water body and application of modularized artificial floating island
CN106242067A (en) * 2016-09-10 2016-12-21 安徽蓝鼎环保能源科技有限公司 A kind of purification method of aquaculture wastewater
CN108178322A (en) * 2018-02-06 2018-06-19 杭州师范大学钱江学院 A kind of spiral shell water shield solid integrated system for controlling body eutrophication
CN108821447A (en) * 2018-07-26 2018-11-16 杭州珊瑚环境科技有限公司 A kind of river Benthic ecology environmental system construction method and its device
CN114702140A (en) * 2022-05-05 2022-07-05 杭州珊瑚环境科技有限公司 Water eutrophication optimization system and method based on ecological floating island
CN117843150A (en) * 2023-02-15 2024-04-09 朱骏卿 A biological water purification circulation system
US12172108B2 (en) 2018-08-16 2024-12-24 Emd Millipore Corporation Closed bioprocessing device

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6447681B1 (en) * 2000-08-07 2002-09-10 Kent Sea Tech Corporation Aquaculture wastewater treatment system and method of making same
CN101905926A (en) * 2010-08-24 2010-12-08 环境保护部华南环境科学研究所 Ecologically adjustable fish reef ecological floating bed device
CN201694895U (en) * 2010-05-24 2011-01-05 河海大学 A three-dimensional coupling device for purifying water
CN102701520A (en) * 2012-05-21 2012-10-03 浙江大学 Device for purifying aquaculture waste water

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6447681B1 (en) * 2000-08-07 2002-09-10 Kent Sea Tech Corporation Aquaculture wastewater treatment system and method of making same
CN201694895U (en) * 2010-05-24 2011-01-05 河海大学 A three-dimensional coupling device for purifying water
CN101905926A (en) * 2010-08-24 2010-12-08 环境保护部华南环境科学研究所 Ecologically adjustable fish reef ecological floating bed device
CN102701520A (en) * 2012-05-21 2012-10-03 浙江大学 Device for purifying aquaculture waste water

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
李先宁等: "组合型生态浮床的动态水质净化特性", 《环境科学》 *
罗思亭等: "沉水植物与生态浮床组合对水产养殖污染控制的研究", 《生态与农村环境学报》 *

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103351086A (en) * 2013-07-30 2013-10-16 中国水产科学研究院渔业机械仪器研究所 Ecological treatment circulatory system for discharge water of sea farming pond
CN103351086B (en) * 2013-07-30 2014-11-26 中国水产科学研究院渔业机械仪器研究所 A kind of marine aquaculture pond discharge water ecological treatment circulation system
CN104003523A (en) * 2014-05-14 2014-08-27 广州中国科学院先进技术研究所 Ecological net cage-based water purification method
CN105906066A (en) * 2016-06-17 2016-08-31 同济大学 Modularized artificial floating island for multi-medium reinforced repair of polluted water body and application of modularized artificial floating island
CN106242067A (en) * 2016-09-10 2016-12-21 安徽蓝鼎环保能源科技有限公司 A kind of purification method of aquaculture wastewater
CN108178322A (en) * 2018-02-06 2018-06-19 杭州师范大学钱江学院 A kind of spiral shell water shield solid integrated system for controlling body eutrophication
CN108821447A (en) * 2018-07-26 2018-11-16 杭州珊瑚环境科技有限公司 A kind of river Benthic ecology environmental system construction method and its device
US12172108B2 (en) 2018-08-16 2024-12-24 Emd Millipore Corporation Closed bioprocessing device
CN114702140A (en) * 2022-05-05 2022-07-05 杭州珊瑚环境科技有限公司 Water eutrophication optimization system and method based on ecological floating island
CN117843150A (en) * 2023-02-15 2024-04-09 朱骏卿 A biological water purification circulation system

Also Published As

Publication number Publication date
CN103193324B (en) 2014-07-02

Similar Documents

Publication Publication Date Title
CN103193324B (en) A purification method for aquaculture sewage and an ecological floating bed based on the method
CN110590061A (en) An ecological purification circulation system suitable for tail water of inland freshwater aquaculture ponds
CN102219332A (en) Novel technology for treating domestic sewage in rural area
CN205648738U (en) All receive and be close to ecological industrialization farming systems of shrimp
CN103351086B (en) A kind of marine aquaculture pond discharge water ecological treatment circulation system
CN105293841B (en) A kind of artificial swamp and filtration system combined depth handles country sewage method and device
CN204400695U (en) Water ecology repair system
CN105432549B (en) A kind of continental rise pond system for having both purifying aquaculture discharge water and breeding function
CN102976494A (en) Multi-habitat ecological pond system
CN108401970A (en) A kind of fish, shrimp, algae, abalone and ginseng circulating water ecological comprehensive breeding system
CN206457304U (en) A kind of imported pollution lake body ecological purification system
CN205794503U (en) A kind of environmental rice fish cycling use of water facility
CN204443674U (en) A kind of circulation
CN104261618B (en) A kind of artificial swamp processed for Tailwater Depth and Plant Pond joint processing system
CN108218131A (en) A kind of ecological canal of coastal tidal aquaculture source water treatment
CN104058506B (en) A kind of freshwater aquaculture water treatment process and multi-functional composite ecologic irrigation canals and ditches
CN204377721U (en) A kind of ecological circulation freshwater aquiculture system
CN107459226A (en) Inland sea farming system and its cultural method
CN208279378U (en) A double circulation seawater prawn comprehensive culture system
CN102838213B (en) Complex organism filtering system
CN110304729A (en) A floating bed for in situ treatment of algae collection
CN206559930U (en) A kind of box breeding consubstantiality ecologic breeding floating bed
CN205472952U (en) Shore protection grass planting water purification bag
CN108821437B (en) An ecological tower for treating eutrophic water body and its application
CN205933534U (en) Ecological interception facility of agricultural non -point source pollution

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20140702

Termination date: 20160419

CF01 Termination of patent right due to non-payment of annual fee