CN205455413U - Surface blowdown and device of administering blue alga oxygenation simultaneously - Google Patents
Surface blowdown and device of administering blue alga oxygenation simultaneously Download PDFInfo
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- CN205455413U CN205455413U CN201620020733.6U CN201620020733U CN205455413U CN 205455413 U CN205455413 U CN 205455413U CN 201620020733 U CN201620020733 U CN 201620020733U CN 205455413 U CN205455413 U CN 205455413U
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- pipe
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- aerator
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- 238000006213 oxygenation reaction Methods 0.000 title description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 34
- 241000192700 Cyanobacteria Species 0.000 claims abstract description 17
- 238000005276 aerator Methods 0.000 claims abstract description 15
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims abstract description 14
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 14
- 239000001301 oxygen Substances 0.000 claims abstract description 14
- 239000013589 supplement Substances 0.000 claims 4
- 238000012258 culturing Methods 0.000 claims 2
- 238000011144 upstream manufacturing Methods 0.000 claims 1
- 239000010865 sewage Substances 0.000 abstract description 25
- 239000002352 surface water Substances 0.000 abstract description 11
- 238000003756 stirring Methods 0.000 abstract description 3
- 238000007599 discharging Methods 0.000 abstract description 2
- 239000002344 surface layer Substances 0.000 abstract description 2
- 241001464430 Cyanobacterium Species 0.000 abstract 1
- 241000195493 Cryptophyta Species 0.000 description 16
- 238000000034 method Methods 0.000 description 15
- 244000144974 aquaculture Species 0.000 description 12
- 238000009360 aquaculture Methods 0.000 description 11
- 239000000126 substance Substances 0.000 description 6
- 241000251468 Actinopterygii Species 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 241000238557 Decapoda Species 0.000 description 2
- 238000010170 biological method Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 239000003344 environmental pollutant Substances 0.000 description 2
- 238000012851 eutrophication Methods 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 230000000813 microbial effect Effects 0.000 description 2
- 238000000053 physical method Methods 0.000 description 2
- 231100000719 pollutant Toxicity 0.000 description 2
- 241000894007 species Species 0.000 description 2
- 241001465754 Metazoa Species 0.000 description 1
- 241000192701 Microcystis Species 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- 239000003463 adsorbent Substances 0.000 description 1
- 238000005273 aeration Methods 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000009395 breeding Methods 0.000 description 1
- 230000001488 breeding effect Effects 0.000 description 1
- 239000013043 chemical agent Substances 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 229910000365 copper sulfate Inorganic materials 0.000 description 1
- ARUVKPQLZAKDPS-UHFFFAOYSA-L copper(II) sulfate Chemical compound [Cu+2].[O-][S+2]([O-])([O-])[O-] ARUVKPQLZAKDPS-UHFFFAOYSA-L 0.000 description 1
- 238000004090 dissolution Methods 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 208000010824 fish disease Diseases 0.000 description 1
- 239000008394 flocculating agent Substances 0.000 description 1
- 238000005189 flocculation Methods 0.000 description 1
- 230000016615 flocculation Effects 0.000 description 1
- 238000003306 harvesting Methods 0.000 description 1
- 230000002401 inhibitory effect Effects 0.000 description 1
- 230000009545 invasion Effects 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 239000013049 sediment Substances 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 208000024891 symptom Diseases 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 238000003911 water pollution Methods 0.000 description 1
Landscapes
- Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)
Abstract
本实用新型公开了一种养殖池塘表面排污和治理蓝藻同时增氧的装置。采取在池塘中央排污处垂直设置排水管插入排水口,排水管上端通过轴承连接90度弯管,弯管再横向连接一段单向开孔排污管,在排污管的末端通过接头连接一台浮于水面的增氧机。本实用新型由于在池塘中央固定有一个立管且不透水,横管上有孔,一半浸没在表层水中,所以拔出外面的排污管后,只有表面的水通过管孔流出,再加上横管在旋转,就把表面的污物全部吸入管中排出。而由于蓝藻一般在水的表层集中,本实用新型可以专一的排出表层水,就可同时排出蓝藻,治理蓝藻。由于增氧机不固定,开动增氧机即推动管沿水面绕中央管旋转,旋转的增氧机和带动的管搅动表面水就可达到增氧的目的。
The utility model discloses a device for simultaneously increasing oxygen on the surface of a culture pond for discharging sewage and treating cyanobacteria. A drainage pipe is installed vertically at the sewage discharge point in the center of the pond to be inserted into the drainage outlet. The upper end of the drainage pipe is connected to a 90-degree elbow through a bearing, and the elbow is then horizontally connected to a section of one-way open sewage pipe. Aerators on the surface of the water. In the utility model, a standpipe is fixed in the center of the pond and is impermeable, and there are holes in the horizontal pipe, half of which is submerged in the surface water, so after the outside sewage pipe is pulled out, only the surface water flows out through the pipe hole, and the horizontal pipe When the tube is rotating, all the dirt on the surface is sucked into the tube and discharged. And because cyanobacteria is generally concentrated in the surface layer of water, the utility model can discharge surface water exclusively, just can discharge cyanobacterium simultaneously, controls cyanobacteria. Since the aerator is not fixed, when the aerator is turned on, the tube is pushed to rotate around the central tube along the water surface, and the rotating aerator and the driven tube stir the surface water to achieve the purpose of increasing oxygen.
Description
技术领域technical field
本实用新型涉及水产养殖领域,尤其涉及养殖池塘表面排污和治理蓝藻同时增氧的装置。The utility model relates to the field of aquaculture, in particular to a device for simultaneously increasing oxygen on the surface of aquaculture ponds for discharging sewage and treating cyanobacteria.
背景技术Background technique
水产养殖过程中,养殖池塘水表面经常有死藻等杂物漂浮在水面,一是影响空气溶氧进入水体,二是容易被鱼虾等水产养殖品种误食而引起中毒。养殖沉积物在池底分解耗氧,释放有毒有害物质,污染水体,导致鱼病频发,饲料转化率低,养殖成本增加,养殖沉积物超过了水体自净能力,造成富营养化,导致养殖水体内源性污染。目前,全国普遍推广池塘底排污方法,将池塘改造成中央排污池塘,采用锅底形结构,就是在池塘中央设一个排污口,通过在塘底埋设PVC管直通到池塘外面,在池塘外面的排污处立有一个PVC管,比池塘水面高,可作为检测池塘水位,排污的时候拔掉立管,水由于水压作用就排出。这种排污方式称为底部排污,能有效改善养殖水质,提高塘鱼品质和产量,但因为只能把底部的水和污物排出,池塘表面的污物还在,蓝藻还在,仍然容易造成夜晚池塘水体缺氧。During the aquaculture process, there are often dead algae and other debris floating on the water surface of the aquaculture pond. First, it will affect the dissolved oxygen in the air to enter the water body, and second, it is easy to be poisoned by aquaculture species such as fish and shrimp. The aquaculture sediment decomposes at the bottom of the pond to consume oxygen, release toxic and harmful substances, and pollute the water body, resulting in frequent fish diseases, low feed conversion rate, and increased aquaculture costs. Endogenous contamination. At present, the method of sewage discharge at the bottom of the pond is widely promoted throughout the country, and the pond is transformed into a central sewage pond. A pot-bottom structure is adopted, that is, a sewage outlet is set in the center of the pond, and the PVC pipe is buried at the bottom of the pond to lead directly to the outside of the pond. The sewage outside the pond There is a PVC pipe in place, which is higher than the water surface of the pond, which can be used to detect the water level of the pond. When the sewage is discharged, the standpipe is pulled out, and the water is discharged due to the water pressure. This method of sewage discharge is called bottom sewage discharge, which can effectively improve the water quality of aquaculture and increase the quality and output of fish in the pond. Pond water lacks oxygen at night.
蓝藻水华是近年来水体不断富营养化的结果,天然湖泊、河流和水产养殖用水中有害藻类水华已成为严重影响水环境质量和水体生态安全的全球性问题,而工农业的急速发展加速了氮磷等富营养盐的排放和水体的富营养化,同时它也严重影响水产养殖业的发展。近几十年来人们对去除藻类水华进行了大量的实验和研究工作 , 一般采用物理法、化学法、换水法除藻、生物处理法、组合工艺法和动物捕食等方法治理。化学除藻技术虽有快速高效除藻的优点 , 但是化学药剂的添加又会给水体带来新的污染。化学法所用药剂有多种,如硫酸铜,该药剂效果短暂,而且它本身也为一种污染物,不宜多次施用。换水法治标不治本。生物方法是利用藻类的天敌及其产生的生长抑制物质对藻类的生长、繁殖进行抑制。这类生物要既能高效快速清除微囊藻又能确保对养殖水体及其他水体不会造成物种入侵的危害,而且对水体本身的微生物群落结构和生态平衡不能产生威胁,目前可用于实际生产应用的除藻菌种制剂市场上很少,大多数仅能停留在实验室阶段。生物方法尤其是微生物溶藻,它的起效时间很慢,而且作用时间长,用到实际水产养殖生产实践中具有一定的难度。利用物理方法除藻例如用容器机械收获藻的方法,难于应用于大面积水体污染的清除(耗时、耗钱)。絮凝沉淀法是通过吸附剂与藻类或藻类与污染物之间的分子引力的作用富集藻类,从而将藻从水体中去除的一种方法。但目前现成的絮凝剂投加量都很大。如果投加小剂量很难达到理想的效果。虽然目前有许多对蓝藻进行治理的方法,但各方法有各自的优缺点,得不到广泛应用。而蓝藻是一种普遍存在的藻类,主要分布在水表层,吸收阳光而迅速繁殖,容易造成夜晚池塘水体缺氧而造成养殖品种死亡。Cyanobacteria blooms are the result of continuous eutrophication of water bodies in recent years. Harmful algae blooms in natural lakes, rivers and aquaculture water have become a global problem that seriously affects the quality of the water environment and the ecological safety of water bodies. The rapid development of industry and agriculture has accelerated The discharge of eutrophic salts such as nitrogen and phosphorus and the eutrophication of water bodies are also seriously affected. At the same time, it also seriously affects the development of aquaculture. In recent decades, people have carried out a lot of experiments and research work on the removal of algae blooms. Generally, physical methods, chemical methods, water exchange methods to remove algae, biological treatment methods, combined technology methods and animal predation are used to treat them. Although the chemical algae removal technology has the advantages of rapid and efficient algae removal, the addition of chemical agents will bring new pollution to the water body. There are many kinds of agents used in chemical methods, such as copper sulfate, which has a short-term effect and is itself a pollutant, so it is not suitable for repeated application. Changing the water method treats the symptoms, not the root cause. The biological method is to use the natural enemies of algae and the growth inhibitory substances produced to inhibit the growth and reproduction of algae. This kind of organisms should not only efficiently and quickly remove Microcystis, but also ensure that it will not cause species invasion hazards to aquaculture water and other water bodies, and it will not pose a threat to the microbial community structure and ecological balance of the water body itself. It can be used in practical production applications at present. There are very few algae-killing strain preparations on the market, and most of them can only stay in the laboratory stage. Biological methods, especially microbial algae dissolution, have a slow onset time and a long duration of action, making it difficult to use in actual aquaculture production practice. Using physical methods to remove algae, such as using containers to mechanically harvest algae, is difficult to apply to the removal of large-area water pollution (time-consuming and costly). The flocculation and sedimentation method is a method for removing algae from water bodies by enriching algae through the molecular attraction between adsorbents and algae or between algae and pollutants. However, the dosage of ready-made flocculants is very large. It is difficult to achieve the desired effect if the dosage is small. Although there are many methods for controlling cyanobacteria, each method has its own advantages and disadvantages and cannot be widely used. And blue-green algae is a kind of ubiquitous algae, mainly distributes in the water surface layer, absorbs the sunlight and reproduces rapidly, easily causes the lack of oxygen in the pond water body at night and causes the cultured species to die.
发明内容Contents of the invention
本实用新型通过一种装置可以同时实现排除表面污物,排除蓝藻和进行池塘中间增氧三种目的。The utility model can simultaneously realize the three purposes of removing surface dirt, removing cyanobacteria and increasing oxygen in the middle of the pond through a device.
本实用新型采取的技术方案是:The technical scheme that the utility model takes is:
一种表面排污和治理蓝藻同时增氧的装置,其特征是:在池塘中央排污处垂直设置排水管插入排水口,排水管上端通过轴承连接90度弯管,弯管再横向连接一段单向开孔排污管,在排污管的末端通过接头连接一台浮于水面的增氧机。A device for simultaneously increasing oxygen on the surface of sewage and controlling blue-green algae, characterized in that a drainage pipe is vertically installed at the sewage discharge point in the center of the pond to be inserted into the drainage outlet, the upper end of the drainage pipe is connected to a 90-degree elbow through a bearing, and the elbow is connected horizontally to a section of one-way opening. The end of the sewage pipe is connected to an aerator floating on the water surface through a joint.
所述排污管的长度根据池塘半径调节,管的一半没入水面,旋转方向一侧开有一排圆孔。The length of the sewage discharge pipe is adjusted according to the radius of the pond, half of the pipe is submerged in the water surface, and a row of round holes is opened on one side of the direction of rotation.
所述增氧机不固定。The aerator is not fixed.
本实用新型的有益效果是 :The beneficial effects of the utility model are:
本实用新型由于在养殖池塘中央固定有一个立管且不透水,横管上有孔,且一半浸没在表层水中,所以拔出外面的排污管后,只有表面的水通过横管上的孔流入,再加上横管在旋转,就把表面的污物全部吸入管中排出。而由于蓝藻一般在水的表层集中,传统的底部排污无法排出表层水,也就无法真正治理蓝藻,泼洒化学药品又容易影响鱼虾生长,本实用新型可以专一的排出表层水及杂物,也就在吸排出表面污物的同时排出蓝藻,治理蓝藻。另外,本实用新型的增氧机不固定,开动增氧机即推动横管沿水面围绕中央管旋转,旋转的增氧机和带动的横管搅动表面水就可达到增氧的目的。本实用新型的方法科学合理,结构简单,功能齐全,集排水和排污、排蓝藻、增氧多重功能于一体,效率高,效果显著,所有功能在养殖过程中全程都可随时实现,生产应用管理十分方便。In the utility model, a standpipe is fixed in the center of the breeding pond and is impermeable, and there are holes in the horizontal pipe, and half of it is submerged in the surface water, so after the outside sewage pipe is pulled out, only the surface water flows in through the hole on the horizontal pipe. , plus the horizontal tube is rotating, all the dirt on the surface is sucked into the tube and discharged. However, because blue-green algae are generally concentrated on the surface of the water, the traditional bottom sewage discharge cannot discharge the surface water, and it is impossible to really control the blue-green algae. Splashing chemicals can easily affect the growth of fish and shrimp. The utility model can specifically discharge the surface water and sundries, It also discharges blue-green algae while sucking out surface dirt, and controls blue-green algae. In addition, the aerator of the utility model is not fixed, and when the aerator is started, the horizontal tube is pushed to rotate around the central tube along the water surface, and the rotating aerator and the driven horizontal tube stir the surface water to achieve the purpose of increasing oxygen. The method of the utility model is scientific and reasonable, simple in structure, and complete in function. Very convenient.
附图说明Description of drawings
图1为本实用新型的结构示意图。Fig. 1 is the structural representation of the utility model.
具体实施方式detailed description
以下结合附图实施例对本实用新型做详细描述。Below in conjunction with accompanying drawing embodiment the utility model is described in detail.
本实用新型装置如下:The utility model device is as follows:
在池塘中央排污处以一个大的PVC排水管1插入排水口,排水管1略低于水面20cm左右,管的高度可通过截断或接头再连接一段管进行调节,再在上端连接一个可旋转的中空轴承2,再在其上连接一个90度弯管3、再横向连接一段PVC排污管4,管的长度同样可通过接头进行调节以满足不同大小池塘要求,在排污管4的末端通过大转小的接头,最后连接到一台小型增氧机5上,增氧机5的电线缆从中间排水管1沿排污管4布线过来,方便旋转,增氧机不固定,开动增氧机则推动排污管4沿水面围绕中央管旋转,排污管4的一半没入水面,旋转方向一侧打有一排圆孔,表面水可从孔口进入,随后流向中央排水管1,流出池塘,达到表面排污和控制蓝藻的目的。另外,常规池塘增氧机一般分布在池塘四个角靠边缘处,中间很少有增氧设施,旋转的增氧机和带动的排污管4搅动表面水可达到增氧的目的。A large PVC drain pipe 1 is inserted into the drain outlet at the sewage discharge point in the center of the pond. The drain pipe 1 is slightly lower than the water surface by about 20cm. Bearing 2, then connect a 90-degree elbow 3, and then connect a section of PVC sewage pipe 4 horizontally. The length of the pipe can also be adjusted through the joint to meet the requirements of different sizes of ponds. Finally, it is connected to a small aerator 5. The electric cable of the aerator 5 is routed from the middle drain pipe 1 along the sewage pipe 4, which is convenient for rotation. The aerator is not fixed. The sewage pipe 4 rotates around the central pipe along the water surface, half of the sewage pipe 4 is submerged in the water surface, and a row of round holes is punched on one side of the rotation direction, and the surface water can enter through the holes, then flow to the central drainage pipe 1, and flow out of the pond to reach the surface sewage and The purpose of controlling cyanobacteria. In addition, conventional pond aerators are generally distributed at the four corners of the pond near the edge, and there are few oxygenation facilities in the middle. The purpose of aeration can be achieved by stirring the surface water with the rotating aerator and the driven sewage pipe 4 .
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
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CN105660515A (en) * | 2016-01-11 | 2016-06-15 | 广西壮族自治区水产科学研究院 | Method and device for carrying out surface blowdown, blue-green alga treatment and oxygenation simultaneously |
CN106577464A (en) * | 2017-01-20 | 2017-04-26 | 安阳市水产技术推广服务中心(安阳市水产科学研究所) | Device for removing harmful algae from surface layer of pool water |
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2016
- 2016-01-11 CN CN201620020733.6U patent/CN205455413U/en not_active Expired - Fee Related
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
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CN105660515A (en) * | 2016-01-11 | 2016-06-15 | 广西壮族自治区水产科学研究院 | Method and device for carrying out surface blowdown, blue-green alga treatment and oxygenation simultaneously |
CN106577464A (en) * | 2017-01-20 | 2017-04-26 | 安阳市水产技术推广服务中心(安阳市水产科学研究所) | Device for removing harmful algae from surface layer of pool water |
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