CN210117272U - Bionic aquatic weed for river regulation - Google Patents

Bionic aquatic weed for river regulation Download PDF

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Publication number
CN210117272U
CN210117272U CN201920432725.6U CN201920432725U CN210117272U CN 210117272 U CN210117272 U CN 210117272U CN 201920432725 U CN201920432725 U CN 201920432725U CN 210117272 U CN210117272 U CN 210117272U
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plastic main
bionic
aquatic weed
main rod
pore passage
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CN201920432725.6U
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杨倩
张克勤
朱明星
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Suzhou Best Color Nano Technology Co Ltd
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Suzhou Best Color Nano Technology Co Ltd
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    • 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

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Abstract

The utility model discloses a bionic aquatic weed for river regulation, which comprises a counterweight bottom plate and a plurality of plastic main rods connected on the counterweight bottom plate, wherein flexible bionic grass filaments are densely distributed on the surface of each plastic main rod; the plastic main rod is internally provided with a vertical pore passage, the surface of the plastic main rod is densely provided with micropores communicated with the pore passage, and an oxygen slow release bag is placed in the pore passage. The bionic aquatic weed for river regulation of the utility model has good flexibility and can swing along with water flow; and can slowly release oxygen for the use of microorganisms, is beneficial to forming a biological film on the bionic grass filaments, and does not need additional aeration.

Description

Bionic aquatic weed for river regulation
Technical Field
The utility model relates to a bionical pasture and water technical field, concretely relates to bionical pasture and water for river course is administered.
Background
At present, the current situation of river pollution and eye surprise in China cause that water shortage and accidents caused by pollution continuously occur, so that the factory is stopped, the agricultural yield is reduced, and even the factory is completely harvested. The treatment of river channels is already slow. In the river course treatment process, the most common and most important mode is ecological treatment by aeration reoxygenation, dissolved oxygen in a water body is improved mainly by aeration, according to the characteristics of microorganisms, organic pollutants are degraded into biochemically harmless carbon dioxide, water and microorganism cells, ammonia nitrogen generates nitrate nitrogen in an aerobic process, then nitrogen is generated in an anoxic and anaerobic environment, phosphorus in the water body is taken as an essential element of a synthetic cell to participate in the synthesis and energy metabolism of the cell and is enriched in the cell, and a sulfur-containing compound generates sulfate radicals, so that the pollutant is removed. The formed biological sludge can fall off and be taken away by water or be sent to a solid waste treatment area through manual cleaning. In the river treatment process, as the water body flows, formed microorganisms for removing pollutants can be continuously formed along with the flow of the water body, but the process is also influenced by other environments, such as pollution degree, water flow velocity, temperature and the like, and simultaneously generated adaptive microorganisms can be continuously taken away along with the flow of the water body, so that the microorganisms are easily interfered in the treatment process and the treatment stability is poor.
The biomembrane method is characterized in that a large number of microorganisms (aerobic bacteria, anaerobic bacteria, facultative bacteria, fungi, protozoa, algae and the like) are attached to the surface of a medium filter material to form a biomembrane, and after sewage is contacted with the biomembrane, the microorganisms in the biomembrane take organic pollutants in the sewage as nutrient substances, degrade organic substances in the metabolic process, and simultaneously proliferate the microorganisms to purify the sewage. Wherein, the inert carrier for providing the attachment growth of the microorganism is called as a filter material or a filler. The biofilm method has some special advantages, such as no sludge backflow, easy operation management, no sludge bulking problem, easy microorganism survival, stable operation and the like. Therefore, the technology of water treatment by using a biofilm is certainly applied to a wide range of industries. The basic conditions for biofilms are (1) the attachment of appropriate microorganisms must be enabled; (2) a large specific surface area is required; (3) a large void fraction is necessary; (4) strong biological, chemical reaction stability and enough mechanical strength are required, and the specific gravity difference with water is small; (5) the price is moderate, and the product can be stably provided.
The biological contact material with the advantages and conditions has greatly different wastewater treatment performance due to different structures of various contact materials. The bionic aquatic weed has all the basic conditions, has other unique advantages and is a high-quality contact material which can completely meet the requirements of various wastewater treatments.
SUMMERY OF THE UTILITY MODEL
The technical problem to be solved by the utility model is to provide a bionic aquatic plant for river regulation, which has good flexibility and can swing along with water flow; and can slowly release oxygen for the use of microorganisms, is beneficial to forming a biological film on the bionic grass filaments, and does not need additional aeration.
In order to solve the technical problem, the utility model provides a bionic aquatic weed for river regulation, which comprises a counterweight bottom plate and a plurality of plastic main rods connected on the counterweight bottom plate, wherein flexible bionic grass filaments are densely distributed on the surface of each plastic main rod; the plastic main rod is internally provided with a vertical pore passage, the surface of the plastic main rod is densely provided with micropores communicated with the pore passage, and an oxygen slow release bag is placed in the pore passage.
The utility model discloses in, the bionical grass silk that the plastics mobile jib is densely covered has very high specific surface area and good biocompatibility, can hold back the nutrient substance in the water simultaneously again to build relatively stable microenvironment on the surface of grass silk, provide superior place for the adhesion growth of microorganism in the water, promoted the self-purification ability of the ecological structure recovery water of water body through the recovery water body of the fast propagation of water microorganism.
In the utility model, the oxygen slow-release bag in the pore of the plastic main rod can continuously release oxygen, thereby greatly increasing the dissolved oxygen in the water body, being beneficial to forming microbial communities on the surface of the bionic grass filaments, recovering the self-purification capacity of the water body and accelerating the purification efficiency of the water body; and moreover, additional aeration and oxygenation are not needed, and the energy consumption is greatly reduced. Preferably, the diameter of the micropores is 0.5-2 mm.
In a preferred embodiment of the present invention, the bionic grass filaments are made of polyvinylidene fluoride fiber, polypropylene fiber or nylon fiber. The polyvinylidene fluoride fiber has positive charges, is easy to adsorb microorganisms with negative charges, and has good elastic recovery effect; the nylon fiber can keep a stable structure even if a large amount of microorganisms are attached; the polypropylene fiber has relatively good hydrophilicity, is easy to capture planktonic substances and maintain high-concentration microorganisms.
In a preferred embodiment of the present invention, the oxygen slow-release bag comprises a spherical waterproof casing, and the waterproof casing is filled with calcium peroxide powder and barium sulfate powder; the waterproof shell is provided with a hole, and the aperture is 0.5-2 mm. Calcium peroxide reacts to produce oxygen when it comes into contact with water. The calcium peroxide powder is mixed with barium sulfate, so that the reaction rate can be reduced, and the slow release effect is achieved. The rate of slow release can be controlled by adjusting the ratio of calcium peroxide to barium sulfate. In addition, the micro-holes are arranged on the plastic main rod and the waterproof shell, so that the slow release rate is further reduced.
In a preferred embodiment of the present invention, the length of the plastic main rod is 1-1.5 m.
In a preferred embodiment of the present invention, the top of the plastic main rod is further connected to a floating ball through a rope.
In a preferred embodiment of the present invention, the counterweight bottom plate further has a plurality of stirring paddles. When the water body flows, the stirring paddle can be driven to stir the water body, so that nutrient substances in the water bottom are stirred and taken up for the utilization of microorganisms, and the rapid propagation of the microorganisms in the water body and the purification of the water body are promoted.
The utility model has the advantages that:
1. the utility model discloses a bionical pasture and water for river course is administered, the bionical grass silk that the plastics mobile jib is densely covered has very high specific surface area and good biocompatibility, can hold back the nutrient substance in the water simultaneously again to build the microenvironment of relatively stable on the surface of grass silk, provide superior place for the adhesion growth of microorganism in the water, promoted the self-purification ability of the ecological structure recovery water of water microorganism through the recovery water body of fast propagation.
2. The utility model discloses a bionical pasture and water for river course is administered, ground oxygen slowly-releasing package in the plastics mobile jib pore can release oxygen continuously to greatly increased the ground dissolved oxygen volume in the water, be favorable to bionical grass silk surface to form the microbial community, has resumeed the self-purification ability of water, has accelerated the efficiency that the water purifies; and moreover, additional aeration and oxygenation are not needed, and the energy consumption is greatly reduced.
3. The utility model has simple structure, low investment cost and convenient use, and can be directly thrown into the river channel; and the oxygen slow-release agent is convenient to recover and can be recycled, and the oxygen slow-release agent can be put into the river channel again after being replaced.
Drawings
FIG. 1 is a schematic structural view of an embodiment of the bionic aquatic weed for river regulation of the present invention;
FIG. 2 is a schematic cross-sectional view of the plastic stem of FIG. 1;
the reference numbers in the figures illustrate: 100. a counterweight bottom plate; 200. a plastic main rod; 210. a duct; 220. a plug; 230. an oxygen slow release bag; 300. bionic grass filaments; 400. a floating ball; 500. the paddle is agitated.
Detailed Description
The present invention is further described with reference to the following drawings and specific embodiments so that those skilled in the art can better understand the present invention and can implement the present invention, but the embodiments are not to be construed as limiting the present invention.
Referring to fig. 1, an embodiment of the bionic aquatic weed for river regulation of the present invention includes a counterweight bottom plate 100, a plurality of plastic main rods 200 connected to the counterweight bottom plate 100, and flexible bionic grass filaments 300 densely distributed on the surface of the plastic main rods 200; the plastic main rod 200 is provided with a vertical pore passage 210 inside, the surface of the plastic main rod is densely provided with micropores communicated with the pore passage 210, and an oxygen slow release bag 230 is arranged in the pore passage 210.
In this embodiment, the biomimetic grass filaments 300 are made of polyvinylidene fluoride fibers. The polyvinylidene fluoride fiber can keep the physical and chemical properties of the material for a long time and can also keep the corresponding strength. And the self has positive charges, so that microorganisms with negative charges are easily adsorbed, and meanwhile, the elastic recovery effect is good.
In this embodiment, the bionic grass filament 300 prepared from polyvinylidene fluoride fibers has extremely high specific surface area and good biocompatibility, and can retain nutrients in the water body, so that a relatively stable microenvironment is created on the surface of the grass filament, a superior place is provided for the attachment growth of microorganisms in the water body, and the self-cleaning capability of the water body is restored through the ecological structure of the restoration water body by the rapid propagation of the microorganisms in the water body.
In this embodiment, the oxygen slow-release bag 230 includes a spherical waterproof casing filled with calcium peroxide powder and barium sulfate powder; the waterproof shell is provided with a hole, and the aperture is 0.5-2 mm. When contacting water, the calcium peroxide can react to generate oxygen and enters the water body through the upper hole of the waterproof shell and the micropores on the plastic main rod 200, so that the dissolved oxygen in the water body is greatly increased, the formation of a microbial community on the surface of the bionic grass filaments 300 is facilitated, the self-purification capacity of the water body is recovered, and the efficiency of water body purification is accelerated; and moreover, additional aeration and oxygenation are not needed, and the energy consumption is greatly reduced.
In the embodiment, the calcium peroxide powder is mixed with the barium sulfate, so that the reaction rate can be reduced, and the slow release effect is achieved. The rate of slow release can be controlled by adjusting the ratio of calcium peroxide to barium sulfate. In addition, the rate of slow release is further reduced by the micro-holes in the plastic stem 200 and the waterproof housing.
In this embodiment, the top of the plastic main rod 200 is further connected with a floating ball 400 through a rope, and the plastic main rod 200 floats in the water body through the floating ball 400. Preferably, the floating ball 400 is located at a depth of 0.5-1 m from the surface of the water body.
In this embodiment, the hole 210 in the plastic stem 200 is open at one end for placing the oxygen slow-release bag 230. Preferably, the well 210 has a removable plug 220. After the bionic aquatic weeds are put into the water body for a period of time and oxygen is released, the bionic aquatic weeds can be recycled, the oxygen slow-release bag 230 is added again, and meanwhile, the sludge on the bionic aquatic weeds 300 can be cleaned incidentally and then put into the water body.
In this embodiment, the counterweight bottom plate 100 is further provided with a plurality of stirring paddles 500. When the water body flows, the stirring paddle 500 is driven to stir the water body, so that the nutrient substances in the water bottom are stirred and taken up for the utilization of the microorganisms, and the rapid propagation of the microorganisms in the water body and the purification of the water body are promoted.
The bionic aquatic weed of the embodiment has the advantages of simple structure, low investment cost and convenient use, and can be directly thrown into a river channel.
The above-mentioned embodiments are merely preferred embodiments for fully illustrating the present invention, and the scope of the present invention is not limited thereto. Equivalent substitutes or changes made by the technical personnel in the technical field on the basis of the utility model are all within the protection scope of the utility model. The protection scope of the present invention is subject to the claims.

Claims (6)

1. A bionic aquatic weed for river regulation is characterized by comprising a counterweight bottom plate and a plurality of plastic main rods connected to the counterweight bottom plate, wherein flexible bionic grass filaments are densely distributed on the surfaces of the plastic main rods; the plastic main rod is internally provided with a vertical pore passage, the surface of the plastic main rod is densely provided with micropores communicated with the pore passage, and an oxygen slow release bag is placed in the pore passage.
2. The bionic aquatic weed for treating the river channel according to claim 1, wherein the bionic grass filaments are prepared from polyvinylidene fluoride fibers, polypropylene fibers or nylon fibers.
3. The biomimetic aquatic weed for river regulation of claim 1, wherein the oxygen slow release package comprises a spherical waterproof shell, and calcium peroxide powder and barium sulfate powder are filled in the waterproof shell; the waterproof shell is provided with a hole, and the aperture is 0.5-2 mm.
4. The bionic aquatic weed for treating the river channel as claimed in claim 1, wherein the length of the plastic main rod is 1-1.5 m.
5. The bionic aquatic weed for treating the river channel as claimed in claim 1, wherein a floating ball is further connected to the top of the plastic main rod through a rope.
6. The bionic aquatic weed for treating the river channel according to claim 1, wherein a plurality of stirring blades are further arranged on the counterweight bottom plate.
CN201920432725.6U 2019-04-01 2019-04-01 Bionic aquatic weed for river regulation Active CN210117272U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201920432725.6U CN210117272U (en) 2019-04-01 2019-04-01 Bionic aquatic weed for river regulation

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Application Number Priority Date Filing Date Title
CN201920432725.6U CN210117272U (en) 2019-04-01 2019-04-01 Bionic aquatic weed for river regulation

Publications (1)

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CN210117272U true CN210117272U (en) 2020-02-28

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111732203A (en) * 2020-06-09 2020-10-02 上海中汇水生态科技有限公司 Artificial aquatic plant water purifying device
CN112520842A (en) * 2020-12-23 2021-03-19 四川清和科技有限公司 Immobilized ecological-based bionic aquatic weed
CN115634479A (en) * 2022-10-28 2023-01-24 无锡海拓环保装备科技有限公司 Sedimentation tank for electroplating wastewater treatment

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111732203A (en) * 2020-06-09 2020-10-02 上海中汇水生态科技有限公司 Artificial aquatic plant water purifying device
CN112520842A (en) * 2020-12-23 2021-03-19 四川清和科技有限公司 Immobilized ecological-based bionic aquatic weed
CN115634479A (en) * 2022-10-28 2023-01-24 无锡海拓环保装备科技有限公司 Sedimentation tank for electroplating wastewater treatment
CN115634479B (en) * 2022-10-28 2023-11-07 无锡海拓环保装备科技有限公司 Sedimentation tank for electroplating wastewater treatment

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Address after: Room 408, Wuluo science and Technology Park, 393 chunshenhu Middle Road, Yuanhe street, Xiangcheng District, Suzhou City, Jiangsu Province

Patentee after: SUZHOU BEST COLOR NANOTECHNOLOGY Co.,Ltd.

Address before: Wuzhong Economic Development Zone in Suzhou City, Jiangsu Province, the River Street 215000 Wuzhong Road No. 1368, building 1, room 437, 426 A418

Patentee before: SUZHOU BEST COLOR NANOTECHNOLOGY Co.,Ltd.