A treatment device and method for mine water inrush

Through the use of grid filtration and multi-media filtration technology combined with the use of transport mechanisms, the problems of heavy membrane system burden and high operation and maintenance costs in mine water inrush treatment are solved, and low-cost and efficient mine water inrush purification and continuous filtration treatment are achieved.

CN119161038BActive Publication Date: 2025-07-18SICHUAN METALLURGICAL EXPLORATION & DESIGN GRP ECOLOGICAL ENVIRONMENT ENG CO LTD
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Patent Information

Application Number
CN202411030548.0
Authority / Receiving Office
CN · China
Patent Type
Patents(China)
Current Assignee / Owner
Filing Date
2024-07-30
Publication Date
2025-07-18
Estimated Expiration
2044-07-30

AI Technical Summary

Technical Problem

The prior art has problems in the mine water inrush treatment that the membrane system is burdened, has high operation and maintenance costs, poor operation stability, and is unable to achieve continuous filtration and purification treatment.

Method used

The process of grating filtration + flocculation-assisted precipitation + inclined tube precipitation + primary pH adjustment precipitation + oil removal precipitation + secondary pH adjustment precipitation + multi-media filtration + disinfection and sterilization is adopted, and the continuous backwash of the multi-media filtration layer is achieved in combination with the transport mechanism, cylinder, linkage mechanism and clamping mechanism.

Benefits of technology

It has achieved low-cost and efficient mine inrush water purification, excellent effluent water quality, which can ensure continuous filtration and purification treatment, reduce operation and maintenance costs, and improve work efficiency and purification efficiency.

✦ Generated by Eureka AI based on patent content.

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Abstract

The present invention relates to the technical field of mine water purification and treatment, and discloses a treatment device and method for mine water, including a grille tank, a flocculation reaction tank, a coagulant aid reaction tank, an inclined tube sedimentation tank, a first adjustment sedimentation tank, an oil removal sedimentation tank, a second adjustment sedimentation tank, a multi-media filtration tank, a flushing tank, a disinfection tank and a clear water tank. Two groups of multi-media filtration layers are provided in the multi-media filtration tank, and one group of multi-media filtration layers is composed of a plurality of media filtration layers. By adopting the process treatment method of "grille filtration + flocculation - coagulant aid precipitation + inclined tube precipitation + primary pH adjustment precipitation + oil removal precipitation + secondary pH adjustment precipitation + multi-media filtration + disinfection and sterilization", the present invention has a simple process, is economical and effective, has good treatment effect, low cost, good effluent water quality, is suitable for popularization and use, and can ensure continuous filtration and purification treatment of mine water, improving work efficiency and purification efficiency.
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Description

Technical Field

[0001] The present invention relates to the technical field of mine water purification treatment, and particularly relates to a treatment device and method for mine water inflow. Background Art

[0002] In China, some mines in the coal production capacity have reached the end of their life cycles, and some coal mines with backward production capacity do not meet the requirements of work safety, or have too high mining costs and serious losses, and will be closed or abandoned. During the mining process, on the one hand, the aquifer, aquitard and water-conducting fault are exposed and damaged, and on the other hand, the surrounding rock strata move and the ground surface subsides, resulting in the phenomenon of groundwater or surface water flowing into the shaft or roadway, which is called mine water inflow.

[0003] At present, in order to alleviate the problem of water supply and demand, it is an inevitable trend to recycle and treat mine sewage and reduce environmental pollution. Due to the scouring of the coal seam and the influence of domestic sewage in the mining process, the suspended solids content in the mine water inflow is high, and it contains a high content of emulsified oil, dissolved oil substances, and also contains iron, manganese, magnesium, calcium, sulfate and various heavy metal ions (such as chromium, lead, copper, zinc, nickel, arsenic, lead, ammonia nitrogen ions), etc.

[0004] In the current common treatment of mine water inflow pollution, mostly lime neutralization precipitation method, simple sludge reflux method, HDS treatment method, redox method, ion exchange method, etc. are used. These processes have their own characteristics, but also have their own drawbacks. Generally, the mine water inflow contains a high content of emulsified oil and dissolved oil substances. Commonly, membrane technologies such as nano-ceramic membranes are used for oil removal, but this will increase the burden on the membrane treatment system, and will also cause serious membrane pollution to the membrane system, affecting the flow efficiency. Moreover, the operation and maintenance cost of the membrane system is high, and the operation stability is poor. Subsequently, it will not only waste precious mine water resources, but also may cause a series of environmental pollution problems; and traditionally, various filter materials are often used to remove heavy metal ions in the mine water inflow. Although the filter material layer can be reused by backwashing, improving the service life of the filter material layer, if the filter material layer needs to be backwashed, then the filtration and purification treatment of the mine water inflow will have to be suspended, and the filtration and purification treatment can only be started again after the backwashing of the filter material layer is completed, reducing the work efficiency and purification efficiency, and unable to achieve continuous filtration and purification treatment of the mine water inflow.

[0005] Therefore, the applicant proposes a treatment device and method for mine water inflow to solve the above problems. Summary of the Invention

[0006] Aiming at the deficiencies of the prior art, the purpose of the present invention is to provide a treatment device and method for mine water inflow.

[0007] To achieve the above object, the present invention adopts the following technical solutions:

[0008] A treatment device for mine water inrush, comprising various reaction tanks, a multi-media filter tank and a flushing tank;

[0009] Wherein, two groups of multi-media filter layers are arranged in the multi-media filter tank, one group of the multi-media filter layers is composed of several media filter layers, and the flushing tank is used for backwashing the multi-media filter layers;

[0010] The tops of the multi-media filter tank and the flushing tank are open, transfer mechanisms are arranged on both sides of the tops of the multi-media filter tank and the flushing tank, a cylinder is installed on the top of the transfer mechanism, the tops of the cylinders on both sides are installed with the same mounting plate, several first connecting plates are installed on the bottom of the mounting plate, a support plate is installed between the two first connecting plates, a linkage mechanism is arranged on the support plate, second connecting plates are installed on both sides of the bottom of the support plate, several partition plates are arranged between the two second connecting plates, clamping mechanisms are arranged between the second connecting plates and the partition plates and between the partition plates and the partition plates, and the linkage mechanism can drive the clamping plates of the clamping mechanisms to approach or move away from each other, and can clamp a group of multi-media filter layers.

[0011] Further, the various reaction tanks include a grille tank, a flocculation reaction tank, a coagulant aid reaction tank, an inclined tube sedimentation tank, a first adjustment sedimentation tank, an oil removal sedimentation tank, a second adjustment sedimentation tank, a multi-media filter tank, a disinfection tank and a clear water tank that are connected in sequence. One side of the grille tank is connected to the inlet pipeline, the flocculation reaction tank is connected to the grille tank through a pipeline, the coagulant aid reaction tank is connected to the lower part of the flocculation reaction tank, the inclined tube sedimentation tank is connected to the upper part of the coagulant aid reaction tank, the first adjustment sedimentation tank is connected to the inclined tube sedimentation tank through a pipeline, the oil removal sedimentation tank is connected to the first adjustment sedimentation tank through a pipeline, the second adjustment sedimentation tank is connected to the upper part of the oil removal sedimentation tank, the multi-media filter tank is connected to the upper part of the second adjustment sedimentation tank, the disinfection tank is connected to the lower part of the multi-media filter tank through a pipeline, the clear water tank is connected to the disinfection tank through a pipeline, one side of the lower part of the clear water tank is connected to the outlet pipeline, and the flushing tank is located between the oil removal sedimentation tank, the multi-media filter tank and the clear water tank.

[0012] Further, a horizontal plate is arranged at the lower part inside the grille tank, and at least two grille meshes are vertically placed on the horizontal plate.

[0013] Further, a demulsifier dosing barrel is arranged on the top of the oil removal sedimentation tank, the emulsion dosing pipe of the demulsifier dosing barrel extends into the oil removal sedimentation tank, an aeration pipe is arranged at the lower part inside the oil removal sedimentation tank, an overflow weir plate is arranged at the upper part inside the oil removal sedimentation tank, an oil-water probe is arranged at the connection between the oil removal sedimentation tank and the second adjustment sedimentation tank, and an oil pump is arranged on the top of the oil removal sedimentation tank, and the oil suction pipe of the oil pump extends into the oil removal sedimentation tank and is located on one side of the oil-water probe.

[0014] Further, a set of the multi-media filter layers includes a first media filter layer, a second media filter layer, a third media filter layer, a fourth media filter layer, and a fifth media filter layer arranged in sequence along the water flow direction, and a plurality of media filter layers of the two sets of multi-media filter layers are arranged in an interleaved manner.

[0015] Further, a plurality of hollow partitions are provided in the flushing tank, a plurality of nozzles are communicated with one side of the hollow partition, and the top of the hollow partition is communicated with the water outlet pipe through a connecting pipe.

[0016] Further, the transfer mechanism includes guide rails located on both sides of the top of the multi-media filter tank and the flushing tank, fixing plates are provided at both ends of the guide rails, a chute is provided in the guide rails, a first threaded rod is rotatably provided in the chute, a threaded block is threadedly connected to the first threaded rod, a moving plate is installed on the threaded block, cylinders are installed on both sides of the moving plate, and one end of the first threaded rod penetrates through one of the fixing plates and is connected to the output end of the first motor.

[0017] Further, the linkage mechanism includes a second motor installed on the mounting plate, a first rotating shaft penetrating through the mounting plate is connected to the output end of the second motor, a first bevel gear is installed on the first rotating shaft, second bevel gears are meshed and connected on both sides of the first bevel gear, a second rotating shaft is connected to the second bevel gear, a third bevel gear is installed at the other end of the second rotating shaft, a third rotating shaft is rotatably installed on the support plate, a fourth bevel gear is installed on the third rotating shaft, the fourth bevel gear meshes with the third bevel gear, a plurality of fourth rotating shafts penetrating through the support plate and rotatably connected to the support plate are provided on both sides of the third rotating shaft, a driving synchronous pulley is installed on the third rotating shaft, a driven synchronous pulley is installed at the top of the fourth rotating shaft, and a synchronous belt is connected between the driving synchronous pulley and the plurality of driven synchronous pulleys.

[0018] Further, the clamping mechanism includes a plurality of second threaded rods respectively rotatably connected to the second connecting plate and a plurality of partition plates, a sixth bevel gear is installed at the other end of the second threaded rod, a fifth bevel gear is installed at the bottom of the fourth rotating shaft, the fifth bevel gear meshes with the sixth bevel gear, a clamping plate is threadedly connected to the second threaded rod, and at least one side of the lower part of the clamping plate is provided with a pressing block.

[0019] According to the above treatment method of the treatment device for mine water inrush, the following steps are included:

[0020] S1: Input the mine water inflow into the grid tank through the water inlet pipe to remove large particulate suspended matter in the water inflow; the preliminarily purified mine water inflow enters the flocculation reaction tank through the pipe, and a flocculant is added for flocculation reaction to form small floccules of suspended matter in the water inflow; the mine water inflow enters the coagulant aid reaction tank from the lower part of the flocculation reaction tank, and a coagulant aid is added for coagulant aid reaction to convert the small floccules into larger floccules; the mine water inflow enters the inclined tube sedimentation tank from the upper part of the coagulant aid reaction tank, and the floccules are separated from the water body through the inclined tube network of the inclined tube sedimentation tank;

[0021] S2: The supernatant of the inclined tube sedimentation tank enters the first adjustment sedimentation tank through the pipe. The pH value of the water is adjusted to 10.3 - 10.8 by adding an alkali agent, and magnesium ions in the water are removed; the adjusted mine water inflow in the first adjustment sedimentation tank enters the oil removal sedimentation tank through the pipe. A demulsifier is added, and air flotation is carried out through aeration to remove oil, and iron and manganese ions in the water are removed; the water after oil removal in the oil removal sedimentation tank overflows into the second adjustment sedimentation tank. The pH value of the water is adjusted to 7.3 - 7.8 by adding an acid agent, and calcium ions in the water are removed; the sludge in the grid tank, flocculation reaction tank, coagulant aid reaction tank, and inclined tube sedimentation tank, as well as the sludge and ion precipitates in the first adjustment sedimentation tank, oil removal sedimentation tank, and second adjustment sedimentation tank, are discharged into the sludge thickening tank. The thickened sludge in the sludge thickening tank is dehydrated by a spiral sludge dewatering machine to achieve solid-liquid separation. The supernatant generated in the sludge thickening tank and the spiral sludge dewatering machine is returned to the grid tank, and the separated sludge is transported out for treatment;

[0022] S3: The adjusted mine water inflow in the second adjustment sedimentation tank flows into the multi-media filter tank through the upper through-hole, and the suspended matter is further removed through the multi-media filter layer, and iron, manganese, magnesium, calcium, sulfate, and various heavy metal ions in the water are effectively removed; the purified mine water inflow in the multi-media filter tank enters the disinfection tank through the pipe, and the water is disinfected and sterilized by adding a disinfectant; the water after disinfection and sterilization in the disinfection tank enters the clear water tank through the pipe, and the water in the clear water tank can be used for daily domestic water, road sprinkling, agricultural irrigation, backwashing, etc.;

[0023] S4: When backwashing is required for the multi-media filtration layer in the multi-media filter, the cylinder descends, driving the mounting plate, the first connecting plate, the support plate, the linkage mechanism, the second connecting plate, the partition plate, and the clamping mechanism to descend as a whole. The linkage mechanism drives the clamping plates of the clamping mechanism to approach each other, clamping the multi-media filtration layer that needs to be backwashed. Then, the cylinder ascends, synchronously driving the multi-media filtration layer to rise. When the multi-media filtration layer leaves the multi-media filter, it is moved to directly above the flushing pool by the transfer mechanism. The cylinder descends to place the multi-media filtration layer that needs to be backwashed into the flushing pool. Water in the clear water tank is transported into the flushing pool for backwashing. At this time, there is still a set of multi-media filtration layers in the multi-media filter that can be used to continue filtering and purifying the mine water inflow. After the backwashing of the multi-media filtration layer in the flushing pool is completed, the backwashed multi-media filtration layer is placed back into the multi-media filter through the above-mentioned clamping and transfer steps. The linkage mechanism drives the clamping plates of the clamping mechanism to move away from each other. The mutually separated clamping plates can clamp another set of multi-media filtration layers and transfer the other set of multi-media filtration layers to the flushing pool for backwashing, ensuring continuous filtering and purification of the mine water inflow.

[0024] Compared with the prior art, the present invention provides a treatment device and method for mine water inflow, having the following beneficial effects:

[0025] 1. The present invention adopts a process treatment method of "grille filtration + flocculation - coagulation precipitation + inclined tube precipitation + primary pH adjustment precipitation + oil removal precipitation + secondary pH adjustment precipitation + multi-media filtration + disinfection and sterilization", with a simple process, being economically effective, having good treatment effects, low costs, and good effluent water quality, and is suitable for popularization and use;

[0026] 2. The present invention uses the method of air flotation for oil removal to remove emulsified oil and dissolved oil substances in the mine water inflow. Without using membrane technology, it reduces the operation and maintenance costs. Through aeration, not only can the oil and water be stratified, but also the iron and manganese ions in the water inflow can be oxidized to generate suspended Fe(OH)3 particles and MnO2 precipitates, facilitating the removal of iron and manganese ions and ensuring the effluent water quality;

[0027] 3. By the coordinated use of the transfer mechanism, cylinder, linkage mechanism, and clamping mechanism, the present invention can clamp a set of multi-media filter layers, transfer them from the multi-media filter tank to the flushing tank for backwashing, facilitating subsequent reuse and reducing maintenance costs. After the backwashing is completed, the multi-media filter layers are clamped and transferred back to the multi-media filter tank. The clamping plates are loosened from this set of multi-media filter layers, and the mutually separated clamping plates can clamp another set of multi-media filter layers, transfer the other set of multi-media filter layers to the flushing tank for backwashing, ensuring that there is at least one set of multi-media filter layers in the multi-media filter tank, guaranteeing continuous filtration and purification treatment of the mine water inflow, and improving work efficiency and purification efficiency. BRIEF DESCRIPTION OF THE DRAWINGS

[0028] Figure 1 is a schematic diagram of the internal top view structure of the present invention;

[0029] Figure 2 is a schematic diagram of the top view structure of the present invention;

[0030] Figure 3 is a schematic diagram of the front view structure of the present invention;

[0031] Figure 4 is a schematic diagram of the structure of the first front view section of the present invention;

[0032] Figure 5 is a schematic diagram of the structure of the second front view section of the present invention;

[0033] Figure 6 is a schematic diagram of the structure of the front view section of the oil removal sedimentation tank of the present invention;

[0034] Figure 7 is a schematic diagram of the structure of the front view section of the multi-media filter tank of the present invention;

[0035] Figure 8 is a schematic diagram of the structure of the front view section of the flushing tank of the present invention;

[0036] Figure 9 is a schematic diagram of the front view structure of the linkage mechanism and the clamping mechanism of the present invention;

[0037] Figure 10 is a schematic diagram of the left view section structure of the transfer mechanism, linkage mechanism, and clamping mechanism of the present invention;

[0038] Figure 11 is a schematic diagram of the top view section structure of the linkage mechanism of the present invention;

[0039] Figure 12 is a schematic diagram of the bottom view structure of the clamping mechanism of the present invention;

[0040] Figure 13 is a schematic diagram of the left view section structure of the transfer mechanism of the present invention.

[0041] Labels in the figure: 1. Grid tank; 101. Horizontal plate; 102. Grid mesh; 2. Flocculation reaction tank; 201. Flocculant dosing barrel; 202. Flocculant dosing pipe; 3. Coagulant aid reaction tank; 301. Coagulant aid dosing barrel; 302. Coagulant aid dosing pipe; 4. Inclined tube sedimentation tank; 401. Vertical plate; 402. Inclined tube network; 5. First adjustment sedimentation tank; 501. Alkali agent dosing barrel; 502. Alkali agent dosing pipe; 6. Oil removal sedimentation tank; 601. Demulsifier dosing barrel; 602. Demulsifier dosing pipe; 603. Aeration pipe; 604. Overflow weir plate; 605. Oil-water probe; 606. Oil pump; 7. Second adjustment sedimentation tank; 701. Acid agent dosing barrel; 702. Acid agent dosing pipe; 703. Scale inhibitor dosing barrel; 704. Scale inhibitor dosing pipe; 8. Multi-media filter tank; 801. First media filter layer; 802. Second media filter layer; 803. Third media filter layer; 804. Fourth media filter layer; 805. Fifth media filter layer; 9. Flushing tank; 901. Hollow partition board; 902. Sprinkler head; 903. Connecting pipe; 10. Disinfection tank; 1001. Disinfectant dosing barrel; 1002. Disinfectant dosing pipe; 11. Clear water tank; 12. Inlet pipeline; 13. Outlet pipeline; 14. Cover plate; 15. Sludge discharge pipe; 16. Mixer; 17. Water pump; 18. Handle; 19. Drain pipe; 20. pH meter; 21. Transfer mechanism; 211. Guide rail; 212. Fixed plate; 213. Chute; 214. First threaded rod; 215. Threaded block; 216. Moving plate; 217. First motor; 218. First guide rod; 22. Cylinder; 23. Mounting plate; 24. First connecting plate; 25. Support plate; 26. Linkage mechanism; 261. Second motor; 262. First rotating shaft; 263. First bevel gear; 264. Second bevel gear; 265. Second rotating shaft; 266. Third bevel gear; 267. Fourth bevel gear; 268. Third rotating shaft; 269. Driving synchronous pulley; 270. Driven synchronous pulley; 271. Synchronous belt; 272. Fourth rotating shaft; 273. Fifth bevel gear; 28. Partition board; 29. Clamping mechanism; 291. Sixth bevel gear; 292. Second threaded rod; 293. Clamping plate; 294. Tightening block; 30. Fixed sleeve; 31. Second guide rod. Detailed implementation mode

[0042] The present invention will be further described below in conjunction with the accompanying drawings and embodiments:

[0043] All the standard parts used in the present invention can be purchased from the market. The special-shaped parts can be customized according to the descriptions in the specification and the attached drawings. The specific connection manners of each part all adopt the conventional means such as bolts, rivets, welding, etc. which are mature in the prior art. The machines, parts and equipment all adopt the conventional models in the prior art. In addition, the circuit connection adopts the conventional connection manner in the prior art, which will not be elaborated herein.

[0044] It should be noted that the orientation or positional relationship indicated by the terms "center", "upper", "lower", "left", "right", "vertical", "horizontal", "inner", "outer", etc. is based on the orientation or positional relationship shown in the drawings. It is only for the convenience of describing the present invention and simplifying the description, rather than indicating or implying that the device or element referred to must have a specific orientation, be constructed and operated in a specific orientation. Therefore, it should not be construed as a limitation to the present invention. In addition, the terms "first", "second", "third", "fourth", "fifth", "sixth" are only used for descriptive purposes and cannot be understood as indicating or implying relative importance.

[0045] In the description of the present invention, it should be noted that unless otherwise clearly specified and defined, the terms "installation", "connection", "connection" should be understood in a broad sense. For example, it can be a fixed connection, a detachable connection, or an integral connection; it can be a mechanical connection or an electrical connection; it can be directly connected or indirectly connected through an intermediate medium, and it can be the communication inside two elements. For those of ordinary skill in the art, the specific meanings of the above terms in the present invention can be understood according to specific situations.

[0046] In the description of the present invention, the meaning of "a plurality of" is two or more, unless otherwise clearly and specifically defined.

[0047] An embodiment of the present invention provides a treatment device for mine water inrush. Refer to Figures 1 to 13 , which includes each reaction tank, a multi-media filter tank 8 and a flushing tank 9;

[0048] Among them, two groups of multi-media filter layers are provided in the multi-media filter tank 8. One group of the multi-media filter layers is composed of several media filter layers. The flushing tank 9 is used to backwash the multi-media filter layers;

[0049] The tops of the multi-media filter tank 8 and the flushing tank 9 are open. Transfer mechanisms 21 are provided on both sides of the tops of the multi-media filter tank 8 and the flushing tank 9, capable of transferring the multi-media filter layer. A cylinder 22 is installed on the top of the transfer mechanism 21, and the tops of the cylinders 22 on both sides are provided with the same mounting plate 23. A number of first connecting plates 24 are installed at the bottom of the mounting plate 23, and the number of the first connecting plates 24 is designed according to the actual situation. A support plate 25 is installed between two of the first connecting plates 24. A linkage mechanism 26 is provided on the support plate 25. Second connecting plates 27 are installed on both sides of the bottom of the support plate 25. A number of partition plates 28 are provided between the two second connecting plates 27. Clamping mechanisms 29 are provided between the second connecting plates 27 and the partition plates 28 and between the partition plates 28 and the partition plates 28. The linkage mechanism 26 can drive the clamping plates 293 of the clamping mechanisms 29 to approach or move away from each other, capable of clamping a group of multi-media filter layers.

[0050] In this embodiment, each reaction tank includes a grille tank 1, a flocculation reaction tank 2, a coagulant aid reaction tank 3, an inclined tube sedimentation tank 4, a first regulating sedimentation tank 5, an oil removal sedimentation tank 6, a second regulating sedimentation tank 7, a multi-media filter tank 8, a disinfection tank 10, and a clear water tank 11 that are connected in sequence. One side of the grille tank 1 is connected to an inlet pipeline 12. The flocculation reaction tank 2 is connected to the grille tank 1 through a pipeline. The coagulant aid reaction tank 3 is connected to the lower part of the flocculation reaction tank 2. The inclined tube sedimentation tank 4 is connected to the upper part of the coagulant aid reaction tank 3. The first regulating sedimentation tank 5 is connected to the inclined tube sedimentation tank 4 through a pipeline. The oil removal sedimentation tank 6 is connected to the first regulating sedimentation tank 5 through a pipeline. The second regulating sedimentation tank 7 is connected to the upper part of the oil removal sedimentation tank 6. The multi-media filter tank 8 is connected to the upper part of the second regulating sedimentation tank 7. The disinfection tank 10 is connected to the lower part of the multi-media filter tank 8 through a pipeline. The clear water tank 11 is connected to the disinfection tank 10 through a pipeline. One side of the lower part of the clear water tank 11 is connected to an outlet pipeline 13. The flushing tank 9 is located between the oil removal sedimentation tank 6, the multi-media filter tank 8, and the clear water tank 11.

[0051] Specifically, the grille tank 1, the flocculation reaction tank 2, the coagulant aid reaction tank 3, the inclined tube sedimentation tank 4, the first regulating sedimentation tank 5, the oil removal sedimentation tank 6, the second regulating sedimentation tank 7, the multi-media filter tank 8, the flushing tank 9, the disinfection tank 10, and the clear water tank 11 are integrally arranged; covers 14 are provided on the tops of the grille tank 1, the flocculation reaction tank 2, the coagulant aid reaction tank 3, the inclined tube sedimentation tank 4, the first regulating sedimentation tank 5, the oil removal sedimentation tank 6, the second regulating sedimentation tank 7, the disinfection tank 10, and the clear water tank 11; the lower parts of the grille tank 1, the flocculation reaction tank 2, the coagulant aid reaction tank 3, the inclined tube sedimentation tank 4, the first regulating sedimentation tank 5, the oil removal sedimentation tank 6, and the second regulating sedimentation tank 7 are funnel-shaped, so that sludge and ionic precipitates accumulate along the inclined inner walls, enabling better external discharge.

[0052] Refer to Figures 1 to 5 Figures 1 to 5 , water pumps 17 are provided on all pipelines, and the water pumps 17 are arranged on the cover plate 14; stirrers 16 are provided on the cover plates 14 of the flocculation reaction tank 2, the coagulant aid reaction tank 3, the first regulating sedimentation tank 5, the second regulating sedimentation tank 7 and the disinfection tank 10, making the reaction faster and more uniform and improving work efficiency. The stirrers 16 are vertical stirrers, which is prior art and will not be elaborated here. pH meters are provided on the cover plates 14 of the first regulating sedimentation tank 5 and the second regulating sedimentation tank 7, and the pH meters extend into the first regulating sedimentation tank 5 and the second regulating sedimentation tank 7 respectively, facilitating the detection of the pH concentration in the water. The lower parts of the coagulant aid reaction tank 3 and the flocculation reaction tank 2 are connected through through-holes; the upper part of the inclined tube sedimentation tank 4 and the coagulant aid reaction tank 3 are connected through through-holes; the upper part of the second regulating sedimentation tank 7 and the oil removal sedimentation tank 6 are connected through through-holes;

[0053] The number of the partition plates 28 and the number of the clamping mechanisms 29 are set according to the number of the medium filtration layers in practice.

[0054] Among them, refer to Figures 1 to 5 Figures 1 to 5 , in this embodiment, sludge discharge pipes 15 are connected to the lower parts of the grille tank 1, the flocculation reaction tank 2, the coagulant aid reaction tank 3, the inclined tube sedimentation tank 4, the first regulating sedimentation tank 5, the oil removal sedimentation tank 6 and the second regulating sedimentation tank 7, and a plurality of drain pipes 19 are connected to the lower part of the flushing tank 9.

[0055] Specifically, sludge pumps are provided on the sludge discharge pipes 15; valves are provided on the drain pipes 19. In this embodiment, the number of the drain pipes 19 is 5.

[0056] Refer to Figure 4 Figure 4 , a flocculant dosing bucket 201 is provided on the cover plate 14 of the flocculation reaction tank 2, and the flocculant dosing pipe 202 of the flocculant dosing bucket 201 extends into the flocculation reaction tank 2; among them, the flocculant includes but is not limited to polyaluminum chloride (PAC), polyaluminum sulfate (PAS), polyferric chloride (PFC), polyferric sulfate (PFS), polysilicate aluminum chloride, polysilicate iron sulfate, polyphosphorus aluminum chloride, polyphosphorus iron chloride, polyacrylamide (PAM), etc., and can be one or more of them. In this embodiment, the flocculant is polyaluminum chloride (PAC). Through the stirring of the stirrer 16, the suspended small particles in the mine water inrush form tiny flocs.

[0057] Refer to Figure 5, on the cover plate 14 of the coagulant aid reaction tank 3, there is a coagulant aid dosing tank 301, and the coagulant aid dosing pipe 302 of the coagulant aid dosing tank 301 extends into the coagulant aid reaction tank 3; among them, the coagulant aid includes but is not limited to sulfuric acid, phosphoric acid, lime, chlorine, polyacrylamide, activated silica, sodium alginate, etc., and can be one or more of them. In this embodiment, the coagulant aid is polyacrylamide (PAM). Through the agitation of the agitator 16, the tiny flocs are transformed into larger flocs.

[0058] Refer to Figure 5 , on one side of the bottom of the cover plate 14 of the inclined tube sedimentation tank 4 close to the through-hole of the coagulant aid reaction tank 3, there is a vertical plate 401. Between the side of the vertical plate 401 far from the through-hole and the inner wall of the inclined tube sedimentation tank 4, there is an inclined tube network 402, so that the flocs are separated from the water body; the inclined tube sedimentation tank 4 adopts a conventional inclined tube sedimentation tank 4 in the market, which is prior art and will not be elaborated here.

[0059] Refer to Figure 4 , on the cover plate 14 of the first adjustment sedimentation tank 5, there is an alkali agent dosing tank 501, and the alkali agent dosing pipe 502 of the alkali agent dosing tank 501 extends into the first adjustment sedimentation tank 5; among them, the alkali agent is sodium hydroxide. Adding sodium hydroxide can extend the reaction time of the flocculant and coagulant aid in the mine water inrush, increase the coagulation particles, so the sedimentation speed is faster, and it can adjust the pH value of the water to 10.3 - 10.8. In a strong alkaline environment, a flocculation precipitation reaction is carried out on the high-concentration magnesium ions in the mine water inrush, so that the magnesium ions generate magnesium hydroxide, which is then precipitated and separated out, removing the magnesium ions in the mine water inrush. The precipitation of magnesium hydroxide can be accelerated by adding a flocculant.

[0060] Refer to Figure 5 , on the cover plate 14 of the second adjustment sedimentation tank 7, there is an acid agent dosing tank 701, and the acid agent dosing pipe 702 of the acid agent dosing tank 701 extends into the second adjustment sedimentation tank 7. On the cover plate 14 of the second adjustment sedimentation tank 7, there is also a scale inhibitor dosing tank 703, and the scale inhibitor dosing pipe 704 of the scale inhibitor dosing tank 703 extends into the second adjustment sedimentation tank 7; among them, the acid agent is dilute sulfuric acid. Adding dilute sulfuric acid adjusts the pH value of the water to 7.3 - 7.8. One purpose is to facilitate the subsequent recycling of water by people, and the second is to produce calcium sulfate precipitation by reacting dilute sulfuric acid with the calcium ions in the mine water inrush to remove the calcium ions in the mine water inrush. The precipitation of calcium sulfate can be accelerated by adding a flocculant; adding a scale inhibitor can prevent calcium sulfate from scaling.

[0061] Refer to Figure 5 , on the cover plate 14 of the disinfection tank 10, there is a disinfectant dosing tank 1001, and the disinfectant dosing pipe 1002 of the disinfectant dosing tank 1001 extends into the disinfection tank 10; among them, the disinfectant is sodium hypochlorite, which disinfects and sterilizes the mine water inrush.

[0062] Refer to Figure 4 andFigure 5 In this embodiment, a horizontal plate 101 is provided at the lower part inside the grid tank 1. At least two grid meshes 102 are vertically placed on the horizontal plate 101, and large-particle suspended matters in the inflowing water are removed through the grid meshes 102.

[0063] Specifically, the horizontal plate 101 does not completely enclose the lower part inside the grid tank 1; an opening for the grid mesh 102 to pass through is provided on the cover plate 14 of the grid tank 1. A handle 18 is provided at the top of the grid mesh 102, which is convenient for the staff to extract the grid mesh 102 for cleaning or replacement. In this embodiment, two grid meshes 102 are provided, which is convenient for alternation to ensure that one grid mesh 102 is inside the grid tank 1, so that the mine inflowing water can be continuously filtered. Two groups of limiting components are provided inside the grid tank 1 above the horizontal plate 101. Each group of limiting components includes four limiting strips. Each group of limiting strips is located on both sides inside the grid tank 1 and is arranged oppositely, that is, two limiting strips are provided on one side, and a limiting groove for limiting and guiding the grid mesh 102 is provided between every two limiting strips, so as to prevent the grid mesh 102 from being installed improperly.

[0064] Refer to Figure 4 and Figure 6 In this embodiment, a demulsifier dosing tank 601 is provided at the top of the oil removal and sedimentation tank 6. The emulsion dosing pipe 602 of the demulsifier dosing tank 601 extends into the oil removal and sedimentation tank 6. An aeration pipe 603 is provided at the lower part inside the oil removal and sedimentation tank 6. An overflow weir plate 604 is provided at the upper part inside the oil removal and sedimentation tank 6 to adjust the overflow speed of the mine inflowing water. An oil-water probe 605 is provided at the connection between the oil removal and sedimentation tank 6 and the second regulating sedimentation tank 7. A oil pump 606 is provided at the top of the oil removal and sedimentation tank 6. The oil suction pipe of the oil pump 606 extends into the oil removal and sedimentation tank 6 and is located on one side of the oil-water probe 605.

[0065] Specifically, an exhaust port is connected to the cover plate 14 of the oil removal sedimentation tank 6; the aeration pipe 603 is connected to an external blower, and a number of micropores are provided on the aeration pipe 603. During operation, under the pressure of the gas, the micropores will automatically open, and the gas will enter the oil removal sedimentation tank 6 to contact the mine water inflow. If the pressure disappears, the micropores on the aeration pipe 603 will automatically close to prevent the mine water inflow from flowing back into the micropores. By using micropore aeration, the gas consumption is small, saving gas usage and improving the mixing effect of the water inflow and the demulsifier, thereby improving the efficiency of oil-water separation; the demulsifier has a better demulsification effect when the pH value is about 10; the oil-water probe 605 is located below the upper through hole of the oil removal sedimentation tank 6; the gas enters the aeration pipe 603 through the blower, and the gas sprays out from the micropores to aerate and demulsify the mine water inflow, and perform air flotation oil removal. The oil in the water inflow is brought to the upper layer of the water inflow with the gas after demulsification. The oil in the upper layer first flows out through the overflow weir plate 604. The oil-water probe 605 first detects the overflowing oil, and then transmits a signal to the oil pump 606 through the controller. The oil pump 606 starts to suck the oil, which is convenient for centralized treatment after the oil is collected. When the oil-water probe 605 detects water, the oil pump 606 stops pumping; and through aeration, the iron and manganese ions in the water inflow are oxidized to generate suspended Fe(OH)3 particles and MnO2 precipitates, which is convenient for removing iron and manganese ions and ensuring the water quality of the effluent.

[0066] Monitoring devices are provided at the flocculant dosing tank 201, coagulant aid dosing tank 301, alkali agent dosing tank 501, demulsifier dosing tank 601, acid agent dosing tank 701 and disinfectant dosing tank 1001, which can monitor the dosing amount of the agents in real time, ensure the timely addition of sufficient agents, and ensure the stable operation of the overall system.

[0067] Refer to Figure 7 , in this embodiment, a group of the multi-media filter layers includes a first media filter layer 801, a second media filter layer 802, a third media filter layer 803, a fourth media filter layer 804 and a fifth media filter layer 805 arranged in sequence along the water flow direction, and several media filter layers of the two groups of multi-media filter layers are arranged in an interlaced manner.

[0068] Specifically, two groups of multi-media filter layers are arranged in sequence along the water flow direction as the first media filter layer 801 of the first group of multi-media filter layers, the first media filter layer 801 of the second group of multi-media filter layers, the second media filter layer 802 of the first group of multi-media filter layers, the second media filter layer 802 of the second group of multi-media filter layers, the third media filter layer 803 of the first group of multi-media filter layers, the third media filter layer 803 of the second group of multi-media filter layers, the fourth media filter layer 804 of the first group of multi-media filter layers, the fourth media filter layer 804 of the second group of multi-media filter layers, the fifth media filter layer 805 of the first group of multi-media filter layers, and the fifth media filter layer 805 of the second group of multi-media filter layers. The distance between adjacent two media filter layers is equal. In this embodiment, there are 10 groups of limiting components in the multi-media filter tank 8. Each group of limiting components includes 4 limiting bars. Each group of limiting bars is located on both sides inside the multi-media filter tank 8 and is arranged oppositely, that is, 2 limiting bars are provided on one side, and a limiting groove for limiting and guiding the media filter layer is provided between every two limiting bars, which is convenient for lifting or placing the media filter layer. The media filter layer is filled with media filter materials, and small holes are provided on the media filter layer. The aperture size of the small holes is smaller than the size of the media filter materials.

[0069] The media filter material of the first media filter layer 801 is natural manganese sand. The natural manganese sand can achieve the purpose of removing harmful substances such as iron, manganese, and arsenic in water. It is processed from high-quality natural manganese ore and has a brown appearance. It has a unique effect on the removal of iron and manganese from groundwater. It has the most ideal grading ratio of water treatment filter materials, enabling it to have the largest specific surface area, the strongest sewage interception ability, the largest oxidation and catalytic effect, and the smallest backwashing loss rate per unit volume.

[0070] The media filter material of the second media filter layer 802 is quartz sand. The quartz sand has a certain removal effect on organic pollutants. It is a hard, wear-resistant, and chemically stable silicate mineral. Its main mineral component is SiO2, and it has a wide source, does not require specific processing procedures, and has a low price.

[0071] The media filter material of the third media filter layer 803 is zeolite. Zeolite widely exists in nature and is an aluminosilicate mineral. The unique structure and crystal chemical properties of zeolite enable it to have characteristics such as adsorption, ion exchange, catalysis, acid and alkali resistance, radiation resistance, and low density. It can absorb ammonia nitrogen, organic matter, and heavy metal ions in water and can effectively reduce the toxicity of hydrogen sulfide at the bottom of the pool.

[0072] The media filter material of the fourth media filter layer 804 is activated carbon. Activated carbon is a black porous solid carbonaceous material. It can effectively adsorb free chlorine, phenol, sulfur, oil, colloid, pesticide residues, and other organic pollutants in water, as well as the recovery of organic solvents. It has functions such as decolorization, purification, impurity removal, deodorization, odor removal, carrier, purification, and recovery.

[0073] The filter medium of the fifth medium filtration layer 805 is ion exchange resin. Ion exchange resin is an insoluble molecular compound with a three-dimensional spatial structure, and its functional groups can react with ions in water to remove sulfates and heavy metal ions in water.

[0074] Through the first medium filtration layer 801, the second medium filtration layer 802, the third medium filtration layer 803, the fourth medium filtration layer 804 and the fifth medium filtration layer 805, suspended solids, radioactive pollutants, etc. in the mine water inrush can also be removed. Finally, through the five-layer medium filtration layer, suspended solids, oil substances, various heavy metal ions, radioactive pollutants, etc. in the mine water inrush can be basically and efficiently removed.

[0075] Refer to Figure 8 , in this embodiment, a plurality of hollow partitions 901 are provided in the flushing tank 9. One side of each hollow partition 901 is communicated with a plurality of spray heads 902, and the top of the hollow partition 901 is communicated with the water outlet pipe 13 through a connecting pipe 903.

[0076] Specifically, in this embodiment, the number of the hollow partitions 901 is 5; 10 groups of limiting components are provided in the flushing tank 9. Each group of limiting components includes 4 limiting bars. Each group of limiting bars is located on both sides inside the flushing tank 9 and is arranged oppositely, that is, 2 limiting bars are provided on one side, and a limiting groove for limiting and guiding the medium filtration layer is arranged between every 2 limiting bars, which is convenient for lifting or placing the medium filtration layer. One hollow partition 901 is arranged between every 2 groups of limiting components, dividing the flushing tank 9 into 6 spaces. The lower parts of 5 spaces corresponding to the limiting components are all communicated with a drain pipe 19; through backwashing, suspended solids, flocs, precipitates, etc. on the five-layer medium filtration layer are flushed out by the backwashing water flow and discharged outside through the drain pipe 19; each space is separated by the hollow partition 901. During backwashing, the purposes of non-repeated pollution and clean cleaning are achieved, which is convenient for subsequent reuse, reduces the maintenance cost, improves the effect of subsequent repeated filtration of various heavy metal ions, and prolongs the service life of the medium filtration layer; preferably, the top of the medium filtration layer can be set as an openable cover body. When the medium filtration layer has been used for a long time and loses the function of removing relevant heavy metal ions, the cover body can be opened to replace the internal filter material, so that the medium filtration layer can continue to be used and the service life of this system is improved.

[0077] Refer to Figure 9 and Figure 13, in this embodiment, the transfer mechanism 21 includes guide rails 211 located on both sides of the tops of the multi-media filter tank 8 and the flushing tank 9. Fixed plates 212 are provided at both ends of the guide rails 211. A chute 213 is provided in the guide rails 211. A first threaded rod 214 is rotatably provided in the chute 213. A threaded block 215 is threadedly connected to the first threaded rod 214. A moving plate 216 is installed on the threaded block 215. Cylinders 22 are installed on both sides of the moving plate 216. One end of the first threaded rod 214 penetrates through one of the fixed plates 212 and is connected to the output end of a first motor 217.

[0078] Specifically, the guide rails 211 are located on the cover plates 14 on both sides of the tops of the multi-media filter tank 8 and the flushing tank 9; the longitudinal section of the guide rails 211 is U-shaped, and a chute 213 is formed therein. Both ends of the first threaded rod 214 are rotatably connected to the fixed plates 212; the moving plate 216 is located above the guide rails 211; a first guide rod 218 parallel to the first threaded rod 214 is further provided in the chute 213. The first guide rod 218 penetrates through the threaded block 215 and is slidably connected to the threaded block 215. By providing the first guide rod 218, the stability of the movement of the moving plate 216 is improved; the number of cylinders 22 is 4, and 2 cylinders 22 are provided on each moving plate 216;

[0079] Start the first motor 217, and the first motor 217 drives the first threaded rod 214 to rotate, thereby driving the threaded block 215 to move along the chute 213, so that the moving plate 216 can move back and forth between the multi-media filter tank 8 and the flushing tank 9.

[0080] Refer to Figures 9 to 12 , in this embodiment, the linkage mechanism 26 includes a second motor 261 installed on the mounting plate 23. A first rotating shaft 262 passing through the mounting plate 23 is connected to the output end of the second motor 261. A first bevel gear 263 is installed on the first rotating shaft 262. Second bevel gears 264 are meshed and connected on both sides of the first bevel gear 263. A second rotating shaft 265 is connected to the second bevel gear 264. A third bevel gear 266 is installed at the other end of the second rotating shaft 265. A third rotating shaft 268 is rotatably installed on the support plate 25. A fourth bevel gear 267 is installed on the third rotating shaft 268. The fourth bevel gear 267 meshes with the third bevel gear 266. A plurality of fourth rotating shafts 272 passing through the support plate 25 and rotatably connected to the support plate 25 are provided on both sides of the third rotating shaft 268. A driving synchronous pulley 269 is installed on the third rotating shaft 268. Driven synchronous pulleys 270 are installed at the tops of the fourth rotating shafts 272. A synchronous belt 271 is connected between the driving synchronous pulley 269 and the plurality of driven synchronous pulleys 270.

[0081] Specifically, the number of the first bevel gears 263 is 1, the number of the second bevel gears 264 is 2, the number of the third bevel gears 266 is 2, and the number of the fourth bevel gears 267 is 2; the number of the first rotating shafts 262 is 1, the number of the second rotating shafts 265 is 2, the number of the third rotating shafts 268 is 2, and the number of the fourth rotating shafts 272 is 12, that is, 6 fourth rotating shafts 272 are arranged on each side of the support plate 25; the first rotating shaft 262, the third rotating shaft 268 and the fourth rotating shaft 272 are all vertically arranged; the second rotating shaft 265 is horizontally arranged; both sides of the first bevel gear 263 are meshed with the upper parts of the second bevel gears 264; the lower part of the third bevel gear 266 is meshed with one side of the fourth bevel gear 267; the number of the driving synchronous pulleys 269 is 2, the number of the synchronous belts 271 is 2, and the number of the driven synchronous pulleys 270 is 12, that is, 6 driven synchronous pulleys 270 are arranged on each side above the support plate 25; fixing sleeves 30 are installed on both sides of the support plate 25, the second rotating shaft 265 passes through the fixing sleeve 30 and is rotatably connected to the fixing sleeve 30, and the second rotating shaft 265 is supported by arranging the fixing sleeve 30; the first connecting plate 24 does not interfere with the synchronous belt 271; in this embodiment, 3 driven synchronous pulleys 270 are symmetrically arranged on both sides of the driving synchronous pulley 269 on the same side.

[0082] Referring to Figures 9 to 12 , in this embodiment, the clamping mechanism 29 includes a plurality of second threaded rods 292 respectively rotatably connected to the second connecting plate 27 and a plurality of partition plates 28. The other ends of the second threaded rods 292 are provided with sixth bevel gears 291. The bottoms of the fourth rotating shafts 272 are provided with fifth bevel gears 273. The fifth bevel gears 273 are meshed with the sixth bevel gears 291. Clamping plates 293 are threadedly connected to the second threaded rods 292. At least one side of the lower part of the clamping plates 293 is provided with abutting blocks 294.

[0083] Specifically, the second threaded rods 292 are rotatably connected to both sides of the partition plate 28, and one of the second connecting plates 27 is rotatably connected to the second threaded rod 292; the second threaded rod 292 is horizontally arranged; the number of the fifth bevel gears 273 is 12, corresponding to the number of the fourth rotating shafts 272; the number of the sixth bevel gears 291 is 22, that is, 11 sixth bevel gears 291 are provided on each side below the support plate 25; the number of the second threaded rods 292 corresponds to the number of the sixth bevel gears 291, that is, the number of the second threaded rods 292 is also 22. Similarly, the number of the clamping plates 293 is also 22. Such a setting is to enable the clamping plates 293 to clamp a group of multi-media filter layers when approaching each other, and to clamp another group of multi-media filter layers when moving away from each other, improving the clamping efficiency, so that five-layer media filter layers of a group of multi-media filter layers can be clamped simultaneously each time, facilitating transportation and backwashing; a pressing block 294 is provided on one side of the lower part of the clamping plate 293 close to the second connecting plate 27 at both ends of the support plate 25, and pressing blocks 294 are provided on both sides of the lower part of the remaining clamping plates 293. The pressing block 294 is flexibly arranged, and a rubber pad is provided on the surface of the pressing block 294 to improve the clamping force.

[0084] On both sides between the two second connecting plates 27, second guide rods 31 are provided. The second guide rods 31 on both sides respectively penetrate through all the clamping plates 293 on the same side and are slidably connected to the clamping plates 293, improving the stability of the movement of the clamping plates 293; preferably, two second guide rods 31 are provided on the same side, respectively located at both ends of the clamping plates 293 on the same side, further improving the stability of the movement of the clamping plates 293.

[0085] The content of suspended solids in the mine water inflow is 500 - 1500 mg / L, the oil value is 30 - 50 mg / L, the magnesium ion is 50 - 70 mg / L, the iron ion is 30 - 60 mg / L, the manganese ion is 5 - 10 mg / L, and the calcium ion is 500 - 600 mg / L.

[0086] The concentration values of each item in the treated clear water are as follows: the content of suspended solids is 2.5 - 10 mg / L, the oil value is 0.1 - 0.5 mg / L, the magnesium ion is 2 - 5 mg / L, the iron ion is 1 - 3 mg / L, the manganese ion is 0.02 - 0.05 mg / L, and the calcium ion is 5 - 15 mg / L. It can be seen from the data that the concentrations of various pollutants in the mine water treated by the method of the present invention have all decreased significantly, enabling the treated clear water to be applied to daily domestic water, road sprinkling, agricultural irrigation, backwashing, etc., facilitating people's use.

[0087] According to the above treatment method of the treatment device for mine water, the following steps are included:

[0088] S1: Input the mine water inflow into the grid tank 1 through the water inlet pipe 12 to remove large particulate suspended matter in the water inflow. The preliminarily purified mine water inflow enters the flocculation reaction tank 2 through a pipe, and a flocculation reaction is carried out by adding PAC, so that small particulate suspended matter in the water inflow forms minute flocs. The mine water inflow enters the coagulant aid reaction tank 3 from the lower part of the flocculation reaction tank 2, and a coagulant aid reaction is carried out by adding PAM, so that the minute flocs are transformed into larger flocs. The mine water inflow enters the inclined tube sedimentation tank 4 from the upper part of the coagulant aid reaction tank 3, and the flocs are separated from the water body through the inclined tube network 402 of the inclined tube sedimentation tank 4.

[0089] S2: The supernatant of the inclined tube sedimentation tank 4 enters the first adjustment sedimentation tank 5 through a pipe. The pH value of the water is adjusted to 10.3 - 10.8 by adding sodium hydroxide, and magnesium ions generate magnesium hydroxide, which precipitates out. The adjusted mine water inflow in the first adjustment sedimentation tank 5 enters the oil removal sedimentation tank 6 through a pipe. By adding a demulsifier, gas enters the aeration pipe 603 through a blower, and the gas sprays out from micropores to carry out aeration demulsification on the mine water inflow for air flotation oil removal. The oil in the water inflow is carried to the upper layer of the water inflow after demulsification by the gas. The oil in the upper layer first flows out through the overflow weir plate 604. The oil water probe 605 first detects the overflowed oil, and then transmits a signal to the oil pump 606 through a controller. The oil pump 606 starts to suck the oil for convenient centralized treatment after collection. When the oil water probe 605 detects water, the oil pump 606 stops pumping. And through aeration, iron and manganese ions in the water inflow are oxidized to generate suspended Fe(OH)3 particles and MnO2 precipitates, which is convenient for removing iron and manganese ions to ensure the water quality of the effluent. The water after oil removal in the oil removal sedimentation tank 6 overflows into the second adjustment sedimentation tank 7. The pH value of the water is adjusted to 7.3 - 7.8 by adding dilute sulfuric acid, and calcium sulfate precipitates are produced with calcium ions in the water inflow for convenient separation. The sludge in the grid tank 1, flocculation reaction tank 2, coagulant aid reaction tank 3 and inclined tube sedimentation tank 4 and the sludge and ion precipitates in the first adjustment sedimentation tank 5, oil removal sedimentation tank 6 and second adjustment sedimentation tank 7 are discharged into the sludge thickening tank. The concentrated sludge in the sludge thickening tank is dehydrated by a spiral sludge dewatering machine to achieve solid-liquid separation. The supernatant generated in the sludge thickening tank and the spiral sludge dewatering machine is refluxed to the grid tank 1, and the supernatant is recycled again so that the water inflow can meet the standards for use. The separated sludge is transported out for treatment and can be incinerated.

[0090] S3: The regulated mine water in the second regulating sedimentation tank 7 flows into the multi-media filter tank 8 through the upper through-holes, and further removes suspended solids through the first media filter layer 801, the second media filter layer 802, the third media filter layer 803, the fourth media filter layer 804 and the fifth media filter layer 805, and effectively removes iron, manganese, magnesium, calcium, sulfate and various heavy metal ions in the water; The purified mine water in the multi-media filter tank 8 enters the disinfection tank 10 through a pipeline, and the water is disinfected by adding sodium hypochlorite; The water after disinfection and sterilization in the disinfection tank 10 enters the clear water tank 11 through a pipeline, and the water in the clear water tank 11 can be used for daily domestic water, road sprinkling, agricultural irrigation, backwashing, etc.;

[0091] S4: When the multi-media filter layer in the multi-media filter pool 8 needs to be backwashed, the cylinder 22 is lowered, driving the mounting plate 23, the first connecting plate 24, the support plate 25, the linkage mechanism 26, the second connecting plate 27, the partition plate 28 and the clamping mechanism 29 to descend as a whole, and by starting the second motor 261, the second motor 261 drives the first rotating shaft 262 to rotate, the first rotating shaft 262 drives the first bevel gear 263 to rotate, the first bevel gear 263 drives the second bevel gears 264 on both sides to rotate, the second bevel gear 264 drives the second rotating shaft 265 and the third bevel gear 266 to rotate, and the third bevel gear 266 drives the fourth The bevel gear 267 rotates, the fourth bevel gear 267 drives the third rotating shaft 268 to rotate, the third rotating shaft 268 drives the active synchronous pulley 269 to rotate, the active synchronous pulley 269 drives the driven synchronous pulley 270 on the same side to rotate synchronously through the synchronous belt 271, the driven synchronous pulley 270 drives the fourth rotating shaft 272 to rotate, the fourth rotating shaft 272 drives the fifth bevel gear 273 to rotate, the fifth bevel gear 273 drives the sixth bevel gear 291 to rotate, the sixth bevel gear 291 drives the second threaded rod 292 to rotate, thereby driving the clamping plates 293 to approach each other, clamping a group of multi-media filter layers that need to be backwashed, and then The cylinder 22 rises and drives the multi-media filter layer to rise synchronously. When the multi-media filter layer leaves the multi-media filter pool 8, the first motor 217 is started and the first motor 217 drives the first threaded rod 214 to rotate, thereby driving the threaded block 215 to move along the slide 213, so that the movable plate 216 can move from the multi-media filter pool 8 to the flushing pool 9, so that the multi-media filter layer is located directly above the flushing pool 9. The cylinder 22 descends and places the multi-media filter layer that needs to be backwashed into the flushing pool 9. By transporting water from the clean water pool 11 to the flushing pool 9 for backwashing, at this time, there is still water in the multi-media filter pool 8. A group of multi-media filter layers can be used to continue filtering and purifying the mine water. After the backwashing of the multi-media filter layer in the flushing tank 9 is completed, the backwashed multi-media filter layer is placed back into the multi-media filter tank 8 through the above-mentioned clamping and transporting steps. The reversal of the second motor 261 drives the clamping plates 293 away from each other. The clamping plates 293 away from each other can clamp another group of multi-media filter layers. At this time, the other group of multi-media filter layers can be transported to the flushing tank 9 for backwashing, thereby ensuring continuous filtering and purification of the mine water, extending the service life of the medium filter layer, and improving the work efficiency and purification efficiency.

[0092] The contents not described in detail in this specification belong to the prior art known to professional and technical personnel in this field.

[0093] The above embodiments are only used to illustrate the technical solutions of the present invention, rather than limiting the protection scope of the invention. Obviously, the described embodiments are only some embodiments of the present invention, rather than all embodiments. Based on these embodiments, all other embodiments obtained by those of ordinary skill in the art without creative efforts belong to the scope of protection of the present invention. Although the present invention has been described in detail with reference to the above embodiments, those of ordinary skill in the art can still, without conflict and without creative efforts, combine, add or delete the features in the embodiments of the present invention according to the circumstances or make other adjustments, so as to obtain different technical solutions that essentially do not depart from the concept of the present invention, and these technical solutions also belong to the scope of protection of the present invention.

Claims

1. A treatment device for mine water inrush, characterized in that, It includes various reaction tanks, a multi-media filter tank (8) and a flushing tank (9); Among them, two groups of multi-media filter layers are provided in the multi-media filter tank (8). One group of the multi-media filter layers consists of several media filter layers. The several media filter layers of the two groups of multi-media filter layers are arranged alternately. The flushing tank (9) is used to backwash the multi-media filter layers; The tops of the multi-media filter tank (8) and the flushing tank (9) are open. Transfer mechanisms (21) are provided on both sides of the tops of the multi-media filter tank (8) and the flushing tank (9). A cylinder (22) is installed at the top of the transfer mechanism (21). The tops of the two cylinders (22) are installed with the same mounting plate (23). Several first connecting plates (24) are installed at the bottom of the mounting plate (23). A support plate (25) is installed between the two first connecting plates (24). A linkage mechanism (26) is provided on the support plate (25). Second connecting plates (27) are installed on both sides of the bottom of the support plate (25). Several partition plates (28) are provided between the two second connecting plates (27). Clamping mechanisms (29) are provided between the second connecting plates (27) and the partition plates (28) and between the partition plates (28). The linkage mechanism (26) can drive the clamping plates (293) of the clamping mechanisms (29) to approach or move away from each other. When the clamping plates (293) approach each other, one group of multi-media filter layers can be clamped. When the clamping plates (293) move away from each other, the other group of multi-media filter layers can be clamped.

2. The treatment device for mine water inrush according to claim 1, wherein, The various reaction tanks include a grille tank (1), a flocculation reaction tank (2), a coagulant aid reaction tank (3), an inclined tube sedimentation tank (4), a first regulating sedimentation tank (5), an oil removal sedimentation tank (6), a second regulating sedimentation tank (7), a disinfection tank (10) and a clear water tank (11). The grille tank (1), the flocculation reaction tank (2), the coagulant aid reaction tank (3), the inclined tube sedimentation tank (4), the first regulating sedimentation tank (5), the oil removal sedimentation tank (6), the second regulating sedimentation tank (7), the multi-media filter tank (8), the disinfection tank (10) and the clear water tank (11) are connected in sequence. One side of the grille tank (1) is connected to an inlet pipeline (12). One side of the lower part of the clear water tank (11) is connected to an outlet pipeline (13). The flushing tank (9) is located between the oil removal sedimentation tank (6), the multi-media filter tank (8) and the clear water tank (11).

3. The treatment device for mine water inrush according to claim 2, characterized in that, A horizontal plate (101) is provided at the lower part inside the grille tank (1). At least two grille meshes (102) are vertically placed on the horizontal plate (101).

4. The treatment device for mine water inrush according to claim 2, characterized in that A demulsifier dosing bucket (601) is provided at the top of the oil removal sedimentation tank (6). An air diffuser pipe (603) is provided at the lower part inside the oil removal sedimentation tank (6). An overflow weir plate (604) is provided at the upper part inside the oil removal sedimentation tank (6). An oil-water probe (605) is provided at the connection between the oil removal sedimentation tank (6) and the second regulating sedimentation tank (7). A submersible pump (606) is provided at the top of the oil removal sedimentation tank (6).

5. The treatment device for mine water inrush according to claim 2, characterized in that One set of the multi-media filter layers includes a first media filter layer (801), a second media filter layer (802), a third media filter layer (803), a fourth media filter layer (804), and a fifth media filter layer (805) arranged in sequence along the water flow direction.

6. The treatment device for mine water inrush according to claim 2, characterized in that, A plurality of hollow partitions (901) are provided in the flushing tank (9). One side of the hollow partition (901) is communicated with a plurality of spray heads (902), and the top of the hollow partition (901) is connected to the water outlet pipe (13) through a connecting pipe (903).

7. The treatment device for mine water inrush according to claim 2, characterized in that The transfer mechanism (21) includes guide rails (211) located on both sides of the tops of the multi-media filter tank (8) and the flushing tank (9). Fixing plates (212) are provided at both ends of the guide rails (211). A chute (213) is provided in the guide rails (211). A first threaded rod (214) is rotatably provided in the chute (213). A threaded block (215) is threadedly connected to the first threaded rod (214). A moving plate (216) is installed on the threaded block (215). The cylinders (22) are installed on both sides of the moving plate (216). One end of the first threaded rod (214) penetrates through one of the fixing plates (212) and is connected to the output end of the first motor (217).

8. The treatment device for mine water inrush according to claim 7, characterized in that, The linkage mechanism (26) includes a second motor (261) installed on the mounting plate (23). A first rotating shaft (262) passing through the mounting plate (23) is connected to the output end of the second motor (261). A first bevel gear (263) is installed on the first rotating shaft (262). Second bevel gears (264) are meshed and connected on both sides of the first bevel gear (263). A second rotating shaft (265) is connected to the second bevel gear (264). A third bevel gear (266) is installed at the other end of the second rotating shaft (265). A third rotating shaft (268) is rotatably installed on the support plate (25). A fourth bevel gear (267) is installed on the third rotating shaft (268). The fourth bevel gear (267) meshes with the third bevel gear (266). A plurality of fourth rotating shafts (272) passing through the support plate (25) and rotatably connected to the support plate (25) are provided on both sides of the third rotating shaft (268). A driving synchronous pulley (269) is installed on the third rotating shaft (268). Driven synchronous pulleys (270) are installed at the tops of the fourth rotating shafts (272). A synchronous belt (271) is connected between the driving synchronous pulley (269) and the plurality of driven synchronous pulleys (270). The first rotating shaft (262), the third rotating shaft (268), and the fourth rotating shafts (272) are all vertically arranged, and the second rotating shaft (265) is horizontally arranged.

9. The treatment device for mine water inrush according to claim 8, characterized in that, The clamping mechanism (29) includes a number of horizontally arranged second threaded rods (292). The second threaded rods (292) are rotatably connected to both sides of the partition plate (28). One of the second connecting plates (27) is rotatably connected to the second threaded rod (292). A sixth bevel gear (291) is installed at the other end of the second threaded rod (292). A fifth bevel gear (273) is installed at the bottom of the fourth rotating shaft (272). The fifth bevel gear (273) meshes with the sixth bevel gear (291). A clamping plate (293) is threadedly connected to the second threaded rod (292). At least one side of the lower part of the clamping plate (293) is provided with a pressing block (294). When the fourth rotating shaft (272) rotates, it drives the fifth bevel gear (273) to rotate. The fifth bevel gear (273) drives the sixth bevel gear (291) to rotate. The sixth bevel gear (291) drives the second threaded rod (292) to rotate, thereby driving the clamping plates (293) to approach or move away from each other.

10. The treatment method of the treatment device for mine water inrush according to any one of claims 1-9, characterized in that, It includes the following steps: S1: Input the mine water inflow into the grille tank (1) through the water inlet pipe (12) to remove large particulate suspended matter in the water inflow. The preliminarily purified mine water inflow enters the flocculation reaction tank (2) and undergoes a flocculation reaction by adding a flocculant. Then the mine water inflow enters the coagulant aid reaction tank (3) and undergoes a coagulant aid reaction by adding a coagulant aid. Then the mine water inflow enters the inclined tube sedimentation tank (4), and the flocs are separated from the water body through the inclined tube network (402) of the inclined tube sedimentation tank (4). S2: The supernatant of the inclined tube sedimentation tank (4) enters the first adjustment sedimentation tank (5), and the pH value of the water is adjusted to 10.3 - 10.8 by adding an alkali agent, and magnesium ions in the water are removed. The mine water inflow passing through the first adjustment sedimentation tank (5) enters the oil removal sedimentation tank (6), and a demulsifier is added, and air flotation oil removal is carried out through aeration, and iron and manganese ions in the water are removed. The water passing through the oil removal sedimentation tank (6) enters the second adjustment sedimentation tank (7), and the pH value of the water is adjusted to 7.3 - 7.8 by adding an acid agent, and calcium ions in the water are removed. The sludge in the grille tank (1), flocculation reaction tank (2), coagulant aid reaction tank (3) and inclined tube sedimentation tank (4) and the sludge and ion precipitates in the first adjustment sedimentation tank (5), oil removal sedimentation tank (6) and second adjustment sedimentation tank (7) are discharged into the sludge thickening tank. S3: The mine water inflow in the second adjustment sedimentation tank (7) flows into the multi-media filtration tank (8), and the suspended matter is further removed through the multi-media filtration layer, and iron, manganese, magnesium, calcium, sulfate and various heavy metal ions in the water are effectively removed. The mine water inflow passing through the multi-media filtration tank (8) enters the disinfection tank (10), and the water is disinfected and sterilized by adding a disinfectant. The water passing through the disinfection tank (10) enters the clear water tank (11). S4: When the multi-media filter layer in the multi-media filter tank (8) needs to be backwashed, the cylinder (22) descends, driving the linkage mechanism (26) and the clamping mechanism (29) to descend as a whole. The clamping plates (293) of the clamping mechanism (29) are driven by the linkage mechanism (26) to approach each other, clamping a set of multi-media filter layers that need to be backwashed. Then, the cylinder (22) ascends, synchronously driving the multi-media filter layer to rise. When the multi-media filter layer leaves the multi-media filter tank (8), it is transported to directly above the flushing tank (9) by the transfer mechanism (21). The cylinder (22) descends to place the multi-media filter layer that needs to be backwashed into the flushing tank (9). Water in the clear water tank (11) is conveyed into the flushing tank (9) for backwashing. At this time, there is another set of multi-media filter layers in the multi-media filter tank (8) that can continue to be used for filtering and purifying the mine water inflow. After the backwashing of the multi-media filter layer in the flushing tank (9) is completed, the backwashed multi-media filter layer is placed back into the multi-media filter tank (8) through the above-mentioned clamping and transfer steps. The clamping plates (293) of the clamping mechanism (29) are driven by the linkage mechanism (26) to move away from each other. The mutually separated clamping plates (293) can clamp another set of multi-media filter layers and transport them to the flushing tank (9) for backwashing, ensuring continuous filtering and purification of the mine water inflow.

Citation Information

Patent Citations

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