Biological interception device for river ecological restoration
By designing a biological interception device that includes piles, guidance ropes, and hanging planting grooves in the river ecological restoration, the problem of large engineering quantity, high construction difficulty and high maintenance costs in traditional methods have been solved. Reduce labor intensity and cost, and effectively repair the river ecosystem.
Patent Information
- Application Number
- CN202422331826.8
- Authority / Receiving Office
- CN · China
- Patent Type
- Utility models(China)
- Current Assignee / Owner
- Filing Date
- 2024-09-24
- Publication Date
- 2025-01-28
- Estimated Expiration
- 2034-09-24
AI Technical Summary
Traditional biological interceptor devices have large engineering volume and high construction difficulty in river ecological restoration. Due to the seasonal growth characteristics of aquatic plants, frequent plants need to be replaced, which increases maintenance costs and labor intensity.
Design a river ecological restoration with biological interception devices. By inserting piles and guiding ropes, a stable framework structure is built. The planting slot is suspended between the guidance rope. Sex plant replacement, reducing salvage and re -planting.
Simplified the deployment and maintenance of biological interception devices, reducing the amount of engineering and construction difficulties, reducing labor intensity and maintenance costs, adapting to different river channel conditions, and realizing the purification of river water quality and the repair of ecosystems.
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Figure CN222411228U_ABST
Abstract
Description
Technical Field
[0001] The utility model relates to the technical field of water purification equipment, in particular to a biological interception device for river ecological restoration. Background Art
[0002] With the acceleration of industrialization and the continuous improvement of urbanization, river ecosystems have suffered severe damage. Problems such as water pollution, biodiversity loss, and degradation of riverine ecological environments are becoming increasingly prominent, making the need for river ecological restoration particularly urgent. Traditional methods of river ecological restoration include physical, chemical, and biological remediation, among which biological remediation has attracted much attention due to its environmentally friendly, economical, and sustainable characteristics. Biological interception devices, as an effective bioremediation technology, utilize the adsorption, absorption, and transformation effects of aquatic plants by setting up interception facilities within the river channel to purify water quality and restore the ecosystem.
[0003] Traditional biological interception devices typically involve driving piles into the riverbed and then fixing a retaining net to the piles to intercept aquatic plants. This process is not only large-scale and difficult to construct, but also wastes a significant amount of manpower and resources. Furthermore, because aquatic plant growth is seasonal, different types of plants need to be replaced in different seasons to maintain optimal restoration results. Traditional biological interception devices require extensive dredging and replanting of aquatic plants during replacement, increasing maintenance costs and labor intensity. Therefore, we propose a biological interception device for river ecological restoration to address these problems. Utility Model Content
[0004] In order to achieve the above-mentioned purpose, the present invention specifically adopts the following technical solutions:
[0005] A biological interception device for river ecological restoration, comprising:
[0006] Piles are driven into the riverbank at intervals.
[0007] A guide rope is provided between two opposing stakes, and the length of the guide rope is adjustable;
[0008] A reeling mechanism is provided on the insertion pile, and is used to reel in the guide rope;
[0009] A planting trough is provided on the river bank and between the two guide ropes, a nylon net is provided in the middle of the bottom of the planting trough, and columnar floats are provided on the outer walls of the other two sides of the planting trough;
[0010] Connectors are provided at the four corners of the planting trough, and are used to prevent the planting trough from being separated from the guide rope;
[0011] A limiting element is provided on the guide rope, and the limiting element is used to limit the front and rear position of the planting trough.
[0012] Furthermore, the winding mechanism includes an annular float and a winding wheel that are slidably sleeved on the stake. The winding wheel is located above the annular float, and the guide rope is wound in the groove of the winding wheel.
[0013] Furthermore, a mother Velcro is bonded to the top of the annular float bag, and a child Velcro that matches the mother Velcro is provided at the bottom of the winding wheel.
[0014] Furthermore, the connecting member includes a connecting rope connected to the corner of the planting trough, and the other end of the connecting rope is provided with a self-locking buckle.
[0015] Furthermore, the limiting part includes an externally threaded tube and a sleeve slidably mounted on the surface of the guide rope, a limiting disk is fixed to one end of the externally threaded tube, and a strip-shaped notch is constructed in a circular array at the other end thereof, the sleeve is threadedly connected to the externally threaded tube, and the end thereof away from the externally threaded tube is conical.
[0016] Furthermore, the planting trough is equipped with fences on both sides perpendicular to the direction of the river.
[0017] Furthermore, sleeves are fixed at the four corners of the planting trough, and the two ends of the columnar float are embedded inside the sleeves.
[0018] Furthermore, the bottom end of the stake is conical, and a pressing plate is fixedly provided on its top.
[0019] The beneficial effects of the utility model are as follows:
[0020] 1. The utility model adopts the design of inserting piles and guiding ropes, which eliminates the need for complicated piling and fixing net operations in the river channel. The main deployment work can be completed by standing by the river channel, which is simpler to operate. The length of the guiding rope is adjustable to adapt to different river channel conditions. The design of connecting parts and limiting parts ensures the stability and safety of the planting trough.
[0021] 2. This utility model constructs a stable frame structure by inserting stakes and guide ropes, and the planting trough is suspended between the guide ropes to form a suspended ecosystem. Aquatic plants grow in the planting trough, and their roots are in contact with the water through the nylon net, absorbing nutrients and pollutants from the water. The planting trough is detachable, which facilitates seasonal plant replacement, reduces a lot of salvage and replanting work, and lowers labor intensity and maintenance costs. Attached Figure Description
[0022] Figure 1 This is a schematic diagram of the three-dimensional structure of the utility model;
[0023] Figure 2This utility model Figure 1 A schematic diagram of the enlarged structure of part A;
[0024] Figure 3 This utility model Figure 1 The enlarged structural diagram of part B in the middle;
[0025] Figure 4 This is a schematic diagram of the planting trough structure of this utility model.
[0026] Figure numerals: 1. Insert pile; 101. Pressing plate; 2. Guide rope; 3. Winding mechanism; 301. Annular float; 302. Winding wheel; 303. Female Velcro; 4. Planting trough; 401. Nylon net; 402. Fence; 403. Sleeve; 404. Columnar float; 5. Connector; 501. Connecting rope; 502. Self-locking buckle; 6. Limiting part; 601. Externally threaded tube; 6011. Strip notch; 602. Sleeve; 603. Limiting disk. DETAILED DESCRIPTION
[0027] In order to make the purpose, technical solutions and advantages of the embodiments of the present invention clearer, the technical solutions in the embodiments of the present invention will be clearly and completely described below in conjunction with the drawings in the embodiments of the present invention.
[0028] This application provides a biological interception device for river ecological restoration, which is mainly used to solve the problems of large engineering workload and high construction difficulty in the existing technology, which requires a lot of manpower and material resources. In addition, due to the seasonal growth of aquatic plants, different types of plants need to be replaced in different seasons to maintain the best restoration effect. When replacing aquatic plants, traditional biological interception devices require a lot of salvaging and replanting work, which increases maintenance costs and labor intensity. The following technical solutions are provided, which will be combined with Figures 1-4 Give detailed instructions:
[0029] A biological interception device for river ecological restoration, comprising:
[0030] Piles 1 are inserted at intervals on the bank of the river;
[0031] Guide rope 2 is set between two opposite stakes 1, and the length of guide rope 2 is adjustable;
[0032] A reeling mechanism 3 is provided on the pile 1 and is used to reel in the guide rope 2;
[0033] Planting trough 4 is set on the riverbank and between two guide ropes 2. A nylon net 401 is set in the middle of the bottom of the planting trough 4, and columnar floats 404 are set on the outer walls of the other two sides of the planting trough 4.
[0034] Connector 5 is located at the four corners of the planting trough 4. Connector 5 is used to prevent the planting trough 4 from detaching from the guide rope 2.
[0035] The limiting member 6 is provided on the guide rope 2 and is used to limit the front and rear positions of the planting trough 4 .
[0036] Workflow Description:
[0037] The first step is to insert piles 1 at intervals on both banks of the river to ensure that the piles 1 are stable;
[0038] Step 2: Set the guide rope 2 between two opposite stakes 1, and adjust the length of the guide rope 2 by the winding mechanism 3 to adapt to the width and depth of the river channel;
[0039] The third step is to set up planting troughs 4 on the riverbank and restrict the planting troughs 4 between two guide ropes 2 using connectors 5 and limiting components 6.
[0040] The fourth step is to plant suitable aquatic plants in planting trough 4. Change the types of plants according to the season. When changing aquatic plants, planting trough 4 can be removed, cleaned, and then new aquatic plants can be planted.
[0041] Working principle:
[0042] The biological interception device constructs a stable frame structure through the insertion piles 1 and the guide ropes 2, and the planting troughs 4 are suspended between the guide ropes 2 to form a suspended ecosystem. Aquatic plants grow in the planting troughs 4, and their roots are in contact with the water body through the nylon mesh 401, absorbing nutrients and pollutants in the water. At the same time, the stems and leaves of the plants are exposed to the water surface to carry out photosynthesis, further purifying the air. As the water flows, the suspended matter and pollutants in the water are adsorbed, absorbed and transformed by the plants, thereby achieving the purpose of purifying the water quality.
[0043] like Figure 2 As shown, in some embodiments, the winding mechanism 3 includes an annular float 301 slidably mounted on the pile 1 and a winding wheel 302. The winding wheel 302 is located above the annular float 301, and the guide rope 2 is wound in the wheel groove of the winding wheel 302. More specifically, the annular float is slidably mounted on the pile 1. This design allows it to move up and down on the pile 1 to adapt to changes in water level. The winding wheel 302 is located above the annular float 301 and is the core part of the winding mechanism 3. A wheel groove is provided on the winding wheel 302 for winding the guide rope 2. By rotating the winding wheel 302, the guide rope 2 can be retracted and released. The guide rope 2 is wound in the wheel groove of the winding wheel 302. The length of the guide rope 2 can be adjusted according to actual needs to adapt to different river conditions.
[0044] like Figure 2As shown, in some embodiments, a female hook and loop fastener 303 is adhered to the top of the annular float 301, and a female hook and loop fastener that cooperates with the female hook and loop fastener 303 is provided at the bottom of the winding reel 302. More specifically, the female hook and loop fastener 303 and the female hook and loop fastener are quickly connected by mutual adsorption. When they are tightly attached, they can form a stable whole, effectively preventing the winding reel 302 and the annular float 301 from separating under the impact of water flow. In addition, after the guide rope 2 is adjusted to a suitable length, the side of the guide rope 2 closest to the winding reel 302 is placed between the annular float 301 and the winding reel 302. The adsorption properties of the female hook and loop fastener 303 and the female hook and loop fastener are used to fix the guide rope 2 between the two, which can prevent the guide rope 2 from continuing to be wound and unwound, ensuring the stability of the planting trough 4.
[0045] like Figure 3 As shown, in some embodiments, the connector 5 includes a connecting rope 501 connected to the corners of the planting trough 4, and the other end of the connecting rope 501 is provided with a self-locking buckle 502. More specifically, one end of the connecting rope 501 is connected to the four corners of the planting trough 4, and the other end is connected to the guide rope 2 via the self-locking buckle 502. This design allows the planting trough 4 to be stably suspended on the guide rope 2, while allowing the planting trough 4 to slide freely on the guide rope 2 to adapt to changes in water flow. The self-locking buckle 502 is a quick-connect and release device, typically used to fix one end to the guide rope 2 and the other end to the connecting rope 501. The design of the self-locking buckle 502 allows for quick adjustment or replacement of the planting trough 4 without disassembling the entire device.
[0046] like Figure 3 As shown, in some embodiments, the limiting member 6 includes an externally threaded tube 601 and a sleeve 602 slidably sleeved on the surface of the guide rope 2. One end of the externally threaded tube 601 is fixed with a limiting disc 603, and its other end has a ring array of strip-shaped notches 6011. The sleeve 602 is threadedly connected to the externally threaded tube 601, and its end away from the externally threaded tube 601 is tapered. More specifically, rotating the limiting disc 603 causes the externally threaded tube 601 and the sleeve 602 to engage. As the threaded connection deepens, the end of the externally threaded tube 601 with the strip-shaped notch 6011 gradually enters the tapered section of the sleeve 602. At this time, the strip-shaped notch 6011 of the externally threaded tube 601 begins to converge, thereby clamping and fixing the guide rope 2. By adjusting the position of the limiting disc 603, it can be ensured that the limiting disc 603 is fixed in the required position, thereby effectively limiting the position of the planting trough 4.
[0047] like Figure 4 As shown, in some embodiments, the planting trough 4 is constructed with fences 402 on both sides perpendicular to the river direction. More specifically, the fences 402 are perpendicular to the river direction. This construction method allows the planting trough 4 to better adapt to the river's flow direction and reduces the impact and erosion of the water flow on the planting trough 4.
[0048] like Figure 4 As shown, in some embodiments, sleeves 403 are fixed at the four corners of the planting trough 4, and the ends of the cylindrical float bladders 404 are embedded in the sleeves 403. More specifically, when the planting trough 4 is placed on the water surface, the cylindrical float bladders 404 provide sufficient buoyancy to support the planting trough 4 and the plants therein. The structure of the sleeves 403 and cylindrical float bladders 404 is relatively simple, making them easy to install and maintain.
[0049] like Figure 1 As shown, in some embodiments, the bottom end of the stake 1 is tapered, and a pressing plate 101 is fixed to its top. More specifically, when inserting the stake 1, the user first aligns the tapered bottom end of the stake 1 with the soil surface and then firmly presses the pressing plate 101. Due to the tapered bottom design, the stake 1 can more easily penetrate the soil surface and penetrate deeper into the soil. At the same time, the pressing plate 101 provides a stable support point for the user, making it easier to apply force.
[0050] The above description of the disclosed embodiments will enable one skilled in the art to implement or use the present invention. Various modifications to these embodiments will be readily apparent to one skilled in the art, and the general principles defined herein may be implemented in other embodiments without departing from the spirit or scope of the present invention. Therefore, the present invention is not limited to the embodiments shown herein but is intended to conform to the widest scope consistent with the principles and novel features disclosed herein.
Claims
1. A biological interception device for river ecological restoration, characterized in that: include: Piles (1) are inserted at intervals on the bank of the river; A guide rope (2) is arranged between two opposite stakes (1), and the length of the guide rope (2) is adjustable; A reeling mechanism (3) is arranged on the plugging pile (1), and the reeling mechanism (3) is used to reel in the guide rope (2); A planting trough (4) is arranged at the river bank and between the two guide ropes (2); a nylon net (401) is arranged in the middle of the bottom of the planting trough (4); and columnar floating bags (404) are arranged on the other two outer walls of the planting trough (4); Connecting pieces (5) are arranged at four corners of the planting groove (4), and the connecting pieces (5) are used to prevent the planting groove (4) from being separated from the guide rope (2); A limiting member (6) is arranged on the guide rope (2), and the limiting member (6) is used to limit the front and rear position of the planting groove (4).
2. A biological interception device for river ecological restoration according to claim 1, characterized in that: The winding mechanism (3) comprises an annular floating bag (301) slidably mounted on the plug pile (1) and a winding wheel (302), wherein the winding wheel (302) is located above the annular floating bag (301), and the guide rope (2) is wound in a wheel groove of the winding wheel (302).
3. A biological interception device for river ecological restoration according to claim 2, characterized in that: A mother Velcro (303) is bonded to the top of the annular floating bag (301), and a child Velcro matching the mother Velcro (303) is provided at the bottom of the winding wheel (302).
4. The biological interception device for river ecological restoration according to claim 1 is characterized in that: The connecting member (5) comprises a connecting rope (501) connected to the corner of the planting groove (4), and the other end of the connecting rope (501) is provided with a self-locking buckle (502).
5. The biological interception device for river ecological restoration according to claim 1 is characterized in that: The limiting member (6) comprises an externally threaded tube (601) and a sleeve (602) which are slidably mounted on the surface of the guide rope (2); a limiting plate (603) is fixedly mounted on one end of the externally threaded tube (601), and a strip-shaped notch (6011) is arranged in a circular array at the other end thereof; the sleeve (602) is threadedly connected to the externally threaded tube (601), and the end thereof away from the externally threaded tube (601) is tapered.
6. The biological interception device for river ecological restoration according to claim 1 is characterized in that: Fences (402) are constructed on both sides of the planting trough (4) that are perpendicular to the river direction.
7. The biological interception device for river ecological restoration according to claim 1 is characterized in that: Sleeves (403) are fixedly provided at the four corners of the planting trough (4), and both ends of the columnar floating bag (404) are embedded in the sleeves (403).
8. The biological interception device for river ecological restoration according to claim 1 is characterized in that: The bottom end of the plug pile (1) is conical, and a pressing plate (101) is fixedly provided on the top thereof.