A seawater pollution purification device and purification method thereof

By designing a seawater pollution purification device and using ozone, hydrogen peroxide and catalyst reaction plates for seawater treatment, the problem of difficulty in removing seawater antibiotics in traditional technologies is solved, and the effect of efficient and multiple purification is achieved.

CN119841439BActive Publication Date: 2025-06-06江苏省连云港环境监测中心
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Patent Information

Application Number
CN202510346949.5
Authority / Receiving Office
CN · China
Patent Type
Patents(China)
Current Assignee / Owner
Filing Date
2025-03-24
Publication Date
2025-06-06
Estimated Expiration
2045-03-24

AI Technical Summary

Technical Problem

Traditional seawater purification processes are difficult to effectively remove antibiotics, resulting in the purified seawater still having a high content of antibiotic components, which requires circulating purification, which has low efficiency and poor effect.

Method used

A seawater pollution purification device is designed, including a reaction chamber, a filtration chamber and a water storage chamber. It uses ozone, hydrogen peroxide and a catalyst reaction plate for seawater treatment, mixes and stirs through a stirring assembly, and uses a multi-layer catalyst reaction plate and a tubular membrane assembly for multiple purifications.

Benefits of technology

By adjusting the pH value of seawater and assisting in the addition of hydrogen peroxide, the reaction efficiency of ozone and antibiotics is improved, and combined with multiple filtration and catalytic reactions, the efficiency and effect of seawater pollution purification are significantly improved.

✦ Generated by Eureka AI based on patent content.

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Abstract

The invention discloses a seawater pollution purification device, which relates to the technical field of seawater pollution purification, and comprises a tank body, wherein a cavity is opened in the tank body, a cylinder body 1 is sleeved in the tank body, a cylinder body 2 is sleeved in the cylinder body 1, both ends of the cylinder body 1 and the cylinder body 2 along the axial direction are sealed with the inner wall of the cavity, a reaction chamber is formed between the cylinder body 1 and the inner wall of the cavity, a filter chamber is formed between the inner wall of the cylinder body 1 and the outer wall of the cylinder body 2, a water storage chamber is formed between the inner wall of the cylinder body 2 and the inner wall of the cavity, a stirring component is arranged in the reaction chamber, the stirring component comprises a fixing ring, a plurality of through holes are opened on the fixing ring, and a plurality of layers of catalyst reaction plates are arranged on the upper side of the fixing ring. The invention has the characteristic of improving the quality of seawater pollution purification.
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Description

Technical Field

[0001] The present invention relates to the technical field of seawater pollution purification, in particular to a seawater pollution purification device and a purification method thereof. Background Art

[0002] Pharmaceuticals and personal care products (PPCPs) are emerging pollutants in the environment, including a variety of chemicals: various medicines (steroids, antibiotics, antipsychotics, lipid-lowering drugs, anti-inflammatory drugs and contraceptives, etc.), disinfectants, facial cleansers, cosmetics, etc.

[0003] Traditional water purification technology: coagulation-sedimentation-filtration-disinfection process is also difficult to effectively remove antibiotics. Currently, the more effective antibiotic purification methods include activated carbon adsorption, chemical oxidation, and membrane separation, but they all use a single treatment equipment for removal. It is difficult to effectively remove the antibiotic components in seawater, resulting in the presence of high levels of antibiotic components in the purified seawater, which needs to be circulated for purification, with low efficiency and poor results.

[0004] Therefore, it is very necessary to design a seawater pollution purification device and a purification method thereof to improve the seawater pollution purification effect. Summary of the invention

[0005] The object of the present invention is to provide a seawater pollution purification device and a purification method thereof to solve the problems raised in the above background technology.

[0006] In order to solve the above technical problems, the present invention provides the following technical solutions: a seawater pollution purification device, comprising a tank body, a cavity is opened in the tank body, a cylinder body 1 is sleeved in the tank body, a cylinder body 2 is sleeved in the cylinder body 1, both ends of the cylinder body 1 and the cylinder body 2 along the axial direction are sealed and connected to the inner wall of the cavity, a reaction cavity is formed between the cylinder body 1 and the inner wall of the cavity, a filtering cavity is formed between the inner wall of the cylinder body 1 and the outer wall of the cylinder body 2, a water storage cavity is formed between the inner wall of the cylinder body 2 and the inner wall of the cavity, and a stirring component is arranged in the reaction cavity;

[0007] The stirring assembly comprises a fixed ring, a plurality of through holes are formed on the fixed ring, a plurality of layers of catalyst reaction plates are arranged on the upper side of the fixed ring, a plurality of connecting rods are fixedly connected to the upper and lower sides of each layer of the catalyst reaction plates, two hinge rods are hinged at both ends of the connecting rods along the axial direction, the two hinge rods corresponding to the upper and lower adjacent catalyst reaction plates are hinged to each other, the lower ends of the two hinge rods on the catalyst reaction plate of the lowest layer are hinged to the fixed ring, the upper sides of the two hinge rods on the catalyst reaction plate of the highest layer are hinged to a connecting ring, and a plurality of electric telescopic rods are fixedly connected to the side of the connecting ring away from the catalyst reaction plate;

[0008] A plurality of groups of annular air pipes are arranged along the axial direction on the circumferential side of the inner wall of the cylinder, and a plurality of exhaust pipes are fixedly connected to the outer circumferential side of the annular air pipes. The exhaust pipes penetrate the cylinder wall away from the annular air pipes and are connected to the reaction chamber for introducing ozone into the reaction chamber.

[0009] According to the above technical solution, a plurality of inlets are opened on the upper side of the cylinder, and filter tubes are arranged in the filter cavity corresponding to the inlets, and the input port of the filter tube is connected to the inlet;

[0010] A plurality of tubular membrane assemblies are sleeved in the filter tube, and an electric-controlled valve 1 is fixedly connected to the upper side of each tubular membrane assembly on the filter tube. A connecting pipe is connected to the upper side of each group of electric-controlled valves 1 and the lower side of the lowest tubular membrane assembly on the filter tube. A side of each connecting pipe away from the filter tube passes through the two cylinder walls of the cylinder and is fixedly connected to a discharge pipe. Each connecting pipe is fixedly connected to an electric-controlled valve 2, and the discharge pipe is located in the water storage chamber.

[0011] According to the above technical solution, the fixing ring is arranged concentrically with the reaction chamber, the inner ring wall and the outer ring wall of the fixing ring are fixedly connected to the outer wall of the cylinder body and the inner wall of the tank body respectively, and the fixing ring is located on the upper side of the uppermost group of annular air pipes;

[0012] A plurality of the through holes are evenly distributed in a circle with the axis of the fixing ring as the center, and a waterproof motor is arranged in each of the through holes. A connecting frame is sleeved on the outer side of the waterproof motor, and the connecting frame is fixedly connected to the inner wall of the through hole on the side away from the waterproof motor, and a stirring blade is fixedly connected to the output end of the waterproof motor.

[0013] According to the above technical solution, a water inlet pipe and a water outlet pipe are fixedly connected to the lower side of the tank body, the output end of the water inlet pipe is connected to the reaction chamber, the input end of the water outlet pipe is connected to the water storage chamber, and a sampler, a pH online detector and a flow control valve are fixedly connected to the water inlet pipe.

[0014] According to the above technical solution, several groups of the annular air pipes are linearly arranged along the axial direction of the cylinder body, and several exhaust pipes are evenly arranged in a circle with the axis of the annular air pipe as the center of the circle, each exhaust pipe is fixedly connected to a one-way air valve, the input end of each group of the annular air pipes is connected to an air intake branch pipe, each of the air intake branch pipes is fixedly connected to a control valve, the input end of each of the air intake branch pipes is commonly connected to an air intake pipe, the input end of the air intake pipe passes through the tank body and is fixedly connected to an air pump, and the input end pipeline of the air pump is connected to an ozone generator.

[0015] According to the above technical solution, an annular water pipe and an annular liquid pipe are arranged on the lower side of the lowest group of annular air pipes in the filter cavity.

[0016] According to the above technical solution, a plurality of drain pipes are fixedly connected to the outer circumference of the annular water pipe, and the plurality of drain pipes are evenly distributed in a circle with the axis of the annular water pipe as the center. The drain pipe is connected to the tube cavity of the annular water pipe, and the side of the drain pipe away from the annular water pipe penetrates the cylinder wall of the cylinder body to connect to the reaction chamber. A one-way valve is fixedly connected to each of the drain pipes, and the one-way valve is located in the filter chamber.

[0017] The input end of the annular water pipe is connected to a liquid inlet pipe 1, the input end of the liquid inlet pipe 1 passes through the tank body and is fixedly connected to a liquid pump 1, the input end pipeline of the liquid pump 1 is connected to a water tank, the water tank contains hydrogen peroxide, and a flow control valve 2 is fixedly connected to the pipeline connecting the liquid pump 1 to the water tank.

[0018] According to the above technical solution, a plurality of drainage pipes are fixedly connected to the outer circumference of the annular liquid pipe, and the plurality of drainage pipes are evenly distributed in a circle with the axis of the annular liquid pipe as the center. The drainage pipe is connected to the tube cavity of the annular liquid pipe, and the side of the drainage pipe away from the annular liquid pipe penetrates through the wall of the cylinder body to connect to the reaction chamber. Each of the drainage pipes is fixedly connected to a second one-way valve, and the second one-way valve is located in the filter chamber.

[0019] The input end of the annular liquid pipe is connected to two liquid inlet pipes 2, and the input end of each of the liquid inlet pipes 2 passes through the tank body and is fixedly connected to a liquid pump 2. The input ends of the two liquid pumps 2 are respectively connected to two liquid tanks by pipelines. The two liquid tanks are respectively filled with an acidic solution and an alkaline solution. Flow control valves 3 are fixedly connected to the pipelines connecting the two liquid pumps 2 to the liquid tanks.

[0020] According to the above technical solution, the purification method of the seawater pollution purification device is:

[0021] S1: sampling and testing the seawater in the water inlet pipe through a sampler, testing the pH value of the seawater in the water inlet pipe through a pH online detector, and determining the content of antibiotics in the seawater and the pH value of the seawater;

[0022] S2: According to the content of antibiotics in seawater, a certain volume of ozone is introduced into the reaction chamber through a corresponding number of annular air pipes from bottom to top, a certain volume of hydrogen peroxide is introduced into the reaction chamber through an annular water pipe, and an acidic solution or an alkaline solution is introduced into the reaction chamber through an annular liquid pipe to maintain the pH value of the seawater at a pH value of A1;

[0023] S3: mixing and stirring seawater, ozone and hydrogen peroxide through a stirring component, and driving the seawater to flow upward;

[0024] S4: By controlling the output end of the electric telescopic rod, a corresponding number of catalyst reaction plates are compressed and moved to below the inlet to participate in the reaction between ozone and antibiotic components in seawater;

[0025] S5: After the reaction is completed, the seawater flows into the filter tube, and is sampled again through the second sampler, and the antibiotic content in the seawater after the reaction is sampled again to determine the antibiotic content in the seawater after the reaction;

[0026] S6: According to the content of antibiotics in the seawater after the reaction, a corresponding number of electric control valves 1 and 2 are closed from bottom to top, so that the seawater is filtered through a corresponding number of tubular membrane modules, flows into the discharge pipe from the connecting pipe on the lower side of the last tubular membrane module passed, and flows into the water storage chamber from the discharge pipe, and finally flows out of the tank through the outlet pipe.

[0027] Compared with the prior art, the beneficial effects achieved by the present invention are as follows: the present invention removes antibiotics by adapting different numbers of annular air pipes and catalyst reaction plates according to the content of antibiotics in seawater;

[0028] By adjusting the pH value of seawater and adding hydrogen peroxide, the reaction efficiency and effect of ozone and antibiotics can be improved, thereby improving the efficiency and effect of seawater pollution purification;

[0029] The seawater after the reaction is purified for a second time by setting filter tubes and a plurality of tubular membrane components, thereby improving the effect of purifying seawater pollution. BRIEF DESCRIPTION OF THE DRAWINGS

[0030] The accompanying drawings are used to provide a further understanding of the present invention and constitute a part of the specification. Together with the embodiments of the present invention, they are used to explain the present invention and do not constitute a limitation of the present invention. In the accompanying drawings:

[0031] Figure 1 It is a schematic diagram of the overall structure of the present invention;

[0032] Figure 2 It is a schematic diagram of the cross-sectional structure of the front side of the tank body of the present invention;

[0033] Figure 3 It is a schematic diagram of the internal structure of the tank body of the present invention;

[0034] Figure 4 It is a schematic diagram of the cross-sectional structure of the annular trachea of ​​the present invention;

[0035] Figure 5 It is a schematic diagram of the stirring assembly and related structures of the present invention;

[0036] Figure 6 It is a schematic diagram of a cross-sectional structure of a part of the cylinder of the present invention;

[0037] Figure 7 It is a schematic diagram of the filter tube split structure and related structures of the present invention;

[0038] In the figure: 1. tank body; 2. support column; 3. cylinder body 1; 4. cylinder body 2; 5. reaction chamber; 6. filter chamber; 7. water storage chamber; 8. water inlet pipe; 9. water outlet pipe; 10. annular air pipe; 11. exhaust pipe; 12. air inlet branch pipe; 13. air inlet pipe; 14. air pump; 15. ozone generator; 16. stirring assembly; 17. fixing ring; 18. through hole; 19. waterproof motor; 20. connecting frame; 21. stirring blade; 22. catalyst reaction plate ; 23. Connecting rod; 24. Hinge rod; 25. Connecting ring; 26. Electric telescopic rod; 27. Annular water pipe; 28. Annular liquid pipe; 29. ​​Drain pipe; 30. Liquid inlet pipe 1; 31. Liquid pump 1; 32. Water tank; 33. Liquid discharge pipe; 34. Liquid inlet pipe 2; 35. Liquid pump 2; 36. Liquid tank; 37. Inlet; 38. Filter tube; 39. Tubular membrane assembly; 40. Electric control valve 1; 41. Connecting pipe; 42. Discharge pipe; 43. Electric control valve 2. DETAILED DESCRIPTION

[0039] The following will be combined with the drawings in the embodiments of the present invention to clearly and completely describe the technical solutions in the embodiments of the present invention. Obviously, the described embodiments are only part of the embodiments of the present invention, not all of the embodiments. Based on the embodiments of the present invention, all other embodiments obtained by ordinary technicians in this field without creative work are within the scope of protection of the present invention.

[0040] See also Figure 1-7 , the present invention provides a technical solution: a seawater pollution purification device, comprising a tank body 1, three support columns 2 are fixedly connected to the lower side of the tank body 1, and are used to stabilize and support the tank body 1;

[0041] like Figure 2 A cavity is provided in the tank body 1, and the cavity is cylindrical. A cylinder body 3 is sleeved in the tank body 1, and a cylinder body 2 4 is sleeved in the cylinder body 1 3. The cylinder body 1 3 and the cylinder body 2 4 are both concentrically arranged with the cavity;

[0042] Both ends of the cylinder 1 3 and the cylinder 2 4 along the axial direction are sealed and connected to the inner wall of the cavity. A reaction chamber 5 is formed between the cylinder 1 3 and the inner wall of the cavity. A filter chamber 6 is formed between the inner wall of the cylinder 1 3 and the outer wall of the cylinder 2 4. A water storage chamber 7 is formed between the inner wall of the cylinder 2 4 and the inner wall of the cavity.

[0043] like Figure 1 The lower side of the tank body 1 is fixedly connected with a water inlet pipe 8 and a water outlet pipe 9, the output end of the water inlet pipe 8 is connected with the reaction chamber 5, and the seawater enters the reaction chamber 5 through the water inlet pipe 8. The water inlet pipe 8 is fixedly connected with a sampler 1, a pH online detector and a flow control valve 1 (not shown in the figure);

[0044] Sampler 1 is used to sample the seawater entering the reaction chamber 5 and determine the content of antibiotics in the seawater through detection. The pH online detector is used to detect the pH value of the seawater. Flow control valve 1 is used to calculate the volume of the seawater entering the reaction chamber 5.

[0045] The input end of the water outlet pipe 9 is connected to the water storage chamber 7 , and the purified seawater enters the water storage chamber 7 and is then discharged from the tank body 1 through the water outlet pipe 9 .

[0046] like Figure 3 A plurality of groups of annular air pipes 10 are arranged along the axial direction on the circumferential side of the inner wall of the cylinder 3, and the plurality of groups of annular air pipes 10 are arranged linearly along the axial direction of the cylinder 3;

[0047] like Figure 4 , a plurality of exhaust pipes 11 are fixedly connected to the outer circumference of the annular air pipe 10, and the plurality of exhaust pipes 11 are evenly distributed in a circle with the axis of the annular air pipe 10 as the center. The exhaust pipes 11 are connected to the lumen of the annular air pipe 10, and the side of the exhaust pipe 11 away from the annular air pipe 10 penetrates the cylinder wall of the cylinder body 3 and connects to the reaction chamber 5. A one-way air valve (not shown in the figure) is fixedly connected to each exhaust pipe 11, and the one-way air valve is located in the filter chamber 6;

[0048] The input end of each group of annular air pipes 10 is connected to an intake branch pipe 12, each intake branch pipe 12 is fixedly connected to a control valve (not shown in the figure), and the input end of each intake branch pipe 12 is commonly connected to an intake pipe 13;

[0049] like Figure 1 The input end of the air inlet pipe 13 passes through the tank body 1 and is fixedly connected to an air pump 14. The input end of the air pump 14 is connected to an ozone generator 15. The ozone generator 15 is conventional technology.

[0050] Ozone is generated by an ozone generator 15, and is passed into the air intake pipe 13 and the air intake branch pipe 12 through an air pump 14. The ozone in the air intake branch pipe 12 is passed into the corresponding annular air pipe 10 by controlling the opening and closing of the control valve on each air intake branch pipe 12. The ozone that has entered the annular air pipe 10 then enters the exhaust pipe 11, and is discharged from the output end of the exhaust pipe 11 through a one-way air valve into the reaction chamber 5 to directly react with the antibiotic components in the seawater.

[0051] According to the content of antibiotics in seawater, ozone is introduced into a corresponding number of annular air tubes 10 from bottom to top to participate in the reaction of the antibiotics in the seawater in the reaction chamber 5. The number of annular air tubes 10 through which ozone is introduced is positively correlated with the content of antibiotics in seawater, that is, the higher the content of antibiotics in seawater, the greater the number of annular air tubes 10 through which ozone is introduced from bottom to top.

[0052] like Figure 5A stirring assembly 16 is provided in the reaction chamber 5, and the stirring assembly 16 includes a fixing ring 17, which is concentrically arranged with the reaction chamber 5, and the inner and outer ring walls of the fixing ring 17 are fixedly connected to the outer wall of the cylinder 3 and the inner wall of the tank body 1, respectively, and the fixing ring 17 is located on the upper side of the uppermost group of annular air pipes 10;

[0053] The fixing ring 17 is provided with a plurality of through holes 18, which are evenly distributed in a circle with the axis of the fixing ring 17 as the center. A waterproof motor 19 is arranged in each through hole 18, and a connecting frame 20 is sleeved on the outer side of the waterproof motor 19. The side of the connecting frame 20 away from the waterproof motor 19 is fixedly connected to the inner wall of the through hole 18. The waterproof motor 19 is conventional technology.

[0054] The output end of the waterproof motor 19 is fixedly connected with a stirring blade 21, and the waterproof motor 19 drives the stirring blade 21 to rotate, so that the seawater and ozone located below the fixing ring 17 are mixed in the through hole 18 through the rotation of the stirring blade 21 and flow through the through hole 18 to the top of the fixing ring 17;

[0055] A plurality of layers of catalyst reaction plates 22 are arranged on the upper side of the fixing ring 17. The catalyst reaction plates 22 are annular, and the inner and outer ring walls of the catalyst reaction plates 22 are in direct contact with the outer wall of the cylinder 3 and the inner wall of the tank 1 respectively;

[0056] A plurality of connecting rods 23 are fixedly connected to the upper and lower sides of each layer of catalyst reaction plates 22. The plurality of connecting rods 23 are evenly distributed in a circle with the axis of the catalyst reaction plate 22 as the center. Two hinge rods 24 are hinged at both ends of the connecting rod 23 along the axis direction. The two hinge rods 24 corresponding to the two adjacent catalyst reaction plates 22 are hinged to each other.

[0057] The lower ends of the two hinge rods 24 on the bottommost group of catalyst reaction plates 22 are hinged to the fixing ring 17, and the upper sides of the two hinge rods 24 on the topmost group of catalyst reaction plates 22 are hinged to a connecting ring 25, and a side of the connecting ring 25 away from the catalyst reaction plate 22 is fixedly connected to a plurality of electric telescopic rods 26, and the plurality of electric telescopic rods 26 are evenly distributed in a circle with the axis of the connecting ring 25 as the center, and the fixed ends of the electric telescopic rods 26 are fixedly connected to the upper inner wall of the cavity;

[0058] By controlling the output end of the electric telescopic rod 26 to extend, the catalyst reaction plates 22 are compressed and moved toward the side of the fixed ring 17, thereby controlling the number of catalyst reaction plates 22 participating in the ozone reaction;

[0059] The mixed seawater and ozone are contacted with the catalyst reaction plate 22 through the through hole 18, and the ozone reacts with the antibiotic components in the seawater under the action of the catalyst, thereby decomposing or converting the antibiotic components in the seawater, thereby achieving the purpose of purifying the seawater.

[0060] like Figure 4 In the filter chamber 6, an annular water pipe 27 and an annular liquid pipe 28 are arranged at the lower side of the lowest group of annular air pipes 10;

[0061] A plurality of drain pipes 29 are fixedly connected to the outer circumference of the annular water pipe 27. The plurality of drain pipes 29 are evenly distributed in a circle with the axis of the annular water pipe 27 as the center. The drain pipes 29 are connected to the lumen of the annular water pipe 27. The side of the drain pipe 29 away from the annular water pipe 27 penetrates the wall of the cylinder body 3 and is connected to the reaction chamber 5. A one-way valve 1 (not shown in the figure) is fixedly connected to each drain pipe 29. The one-way valve 1 is located in the filter chamber 6.

[0062] like Figure 1 The input end of the annular water pipe 27 is connected to a liquid inlet pipe 30, the input end of the liquid inlet pipe 30 penetrates the tank body 1 and is fixedly connected to a liquid pump 31, the input end pipeline of the liquid pump 31 is connected to a water tank 32, the water tank 32 contains hydrogen peroxide, and a flow control valve 2 (not shown in the figure) is fixedly connected to the pipeline connecting the liquid pump 31 to the water tank 32, which is used to control the total volume of hydrogen peroxide injected into the reaction chamber 5, and the hydrogen peroxide is used to cooperate with ozone to react with the antibiotic components in the seawater;

[0063] like Figure 4 A plurality of drain pipes 33 are fixedly connected to the outer circumference of the annular liquid pipe 28. The plurality of drain pipes 33 are evenly distributed around the annular liquid pipe 28 with the axis of the annular liquid pipe 28 as the center. The drain pipes 33 are connected to the lumen of the annular liquid pipe 28. The side of the drain pipe 33 away from the annular liquid pipe 28 penetrates the wall of the cylinder 3 and is connected to the reaction chamber 5. Each drain pipe 33 is fixedly connected to a one-way valve 2 (not shown in the figure), and the one-way valve 2 is located in the filter chamber 6.

[0064] like Figure 1 The input end of the annular liquid pipe 28 is connected to two liquid inlet pipes 2 34, and the input end of each liquid inlet pipe 2 34 passes through the tank body 1 and is fixedly connected to a liquid pump 2 35, and the input ends of the two liquid pumps 2 35 are respectively connected to two liquid tanks 36 by pipelines, and the two liquid tanks 36 are respectively filled with an acidic solution and an alkaline solution, and the acidic solution and the alkaline solution are used to adjust the overall pH value of the seawater in the reaction chamber 5;

[0065] The pipelines connecting the two liquid pumps 2 35 to the liquid tank 36 are fixedly connected with flow control valves 3 (not shown in the figure) for controlling the total volume of liquid injected into the reaction chamber 5 .

[0066] like Figure 6, a plurality of inlets 37 are provided on the upper side of the cylinder 1 3, and the plurality of inlets 37 are evenly distributed in a circle with the axis of the cylinder 1 3 as the center. A filter tube 38 is provided in the filter chamber 6 corresponding to the inlet 37, and the input port of the filter tube 38 is connected to the inlet 37. A sampler 2 (not shown in the figure) is fixedly connected to the input port of the filter tube 38, and the sampler 2 is used for secondary sampling and detection of the seawater flowing into the filter tube 38;

[0067] like Figure 7 The filter tube 38 is provided with a plurality of tubular membrane assemblies 39, which are conventional technologies and are used to filter and remove antibiotic components in seawater;

[0068] Several tubular membrane assemblies 39 are arranged linearly along the axial direction of the filter chamber 6. An electric control valve 40 is fixedly connected to the upper side of each tubular membrane assembly 39 on the filter tube 38. The upper side of each group of electric control valves 40 and the lower side of the lowest tubular membrane assembly 39 on the filter tube 38 are connected with a connecting pipe 41. The side of each connecting pipe 41 away from the filter tube 38 penetrates the wall of the cylinder body 2 4 and is fixedly connected to a discharge pipe 42. Each connecting pipe 41 is fixedly connected to an electric control valve 2 43.

[0069] According to the content of antibiotic components in the seawater, after being filtered through a corresponding number of tubular membrane modules 39, the seawater flows into the discharge pipe 42 from the connecting pipe 41 at the lower side of the last tubular membrane module 39 passed through, and then flows into the water storage chamber 7 from the discharge pipe 42;

[0070] The number of tubular membrane modules 39 that the seawater passes through is positively correlated with the antibiotic content in the seawater, that is, the higher the antibiotic content in the seawater, the greater the number of tubular membrane modules 39 that the seawater passes through.

[0071] In this embodiment, the seawater to be purified is introduced into the reaction chamber 5 through the water inlet pipe 8, and the sample is taken through the sampler 1 to detect the content of antibiotics in the seawater to be purified. At the same time, a certain volume of ozone is introduced into the corresponding number of annular air pipes 10 from bottom to top according to the content of antibiotics in the seawater;

[0072] The number of annular air pipes 10 through which ozone is introduced is positively correlated with the content of antibiotics in seawater, that is, the higher the content of antibiotics in seawater, the more annular air pipes 10 through which ozone is introduced;

[0073] At the same time, a certain volume of hydrogen peroxide is introduced according to the content of antibiotics in the seawater, and according to the pH value of the seawater detected by the pH online detector, the corresponding liquid pump 35 is started to introduce an acidic solution or an alkaline solution into the annular liquid pipe 28 to maintain the pH value of the seawater at a pH value of A1, thereby improving the reaction effect of ozone and the antibiotic components in the seawater.

[0074] After being mixed and stirred by the stirring assembly 16, the seawater, ozone and hydrogen peroxide continue to flow upward and contact the catalyst reaction plate 22;

[0075] According to the antibiotic content in the seawater, the output end of the electric telescopic rod 26 is controlled to be extended or retracted accordingly, so that the catalyst reaction plates 22 of the corresponding number of layers are compressed and moved to the bottom of the inlet 37, and cooperate with ozone to complete the reaction with the antibiotic components in the seawater;

[0076] The number of catalyst reaction plates 22 involved in the reaction is positively correlated with the content of antibiotics in seawater, that is, the higher the content of antibiotics in seawater, the more catalyst reaction plates 22 involved in the reaction;

[0077] After the reaction is completed, the seawater enters the filter tube 38 through the inlet 37, and the seawater after the reaction is sampled and tested for the second time through the sampler 2. According to the antibiotic content measured after sampling, the corresponding number of electric control valves 1 40 and electric control valves 2 43 are closed from bottom to top, so that the seawater is filtered through the corresponding number of tubular membrane modules 39, and then flows into the discharge pipe 42 from the connecting pipe 41 on the lower side of the last tubular membrane module 39 passed through, and flows into the water storage chamber 7 from the discharge pipe 42, thereby completing the secondary purification of the antibiotics in the seawater, and the seawater entering the water storage chamber 7 flows out of the tank body 1 through the outlet pipe 9.

[0078] A purification method for a seawater pollution purification device:

[0079] S1: sampling and testing the seawater in the water inlet pipe 8 through a sampler, testing the pH value of the seawater in the water inlet pipe 8 through a pH online detector, and determining the content of antibiotics in the seawater and the pH value of the seawater;

[0080] S2: According to the content of antibiotics in seawater, a certain volume of ozone is introduced into a corresponding number of annular air pipes 10 from bottom to top, so that the ozone enters the reaction chamber 5, a certain volume of hydrogen peroxide is introduced into the reaction chamber 5 through the annular water pipe 27, and an acidic solution or an alkaline solution is introduced into the reaction chamber 5 through the annular liquid pipe 28, so that the pH value of the seawater is maintained at a pH value of A1;

[0081] S3: mixing and stirring the seawater, ozone and hydrogen peroxide through the stirring assembly 16, and driving the seawater to flow upward;

[0082] S4: Control the output end of the electric telescopic rod 26 to control the corresponding number of catalyst reaction plates 22 to be compressed and moved to below the inlet 37 to participate in the reaction between ozone and antibiotic components in seawater;

[0083] S5: After the reaction is completed, the seawater flows into the filter tube 38, and is sampled again by the second sampler, and the antibiotic content in the seawater after the reaction is sampled again to determine the antibiotic content in the seawater after the reaction;

[0084] S6: According to the content of antibiotics in the seawater after the reaction, a corresponding number of electrically controlled valves 1 40 and electrically controlled valves 2 43 are closed from bottom to top, so that the seawater is filtered through a corresponding number of tubular membrane modules 39, flows into the discharge pipe 42 from the connecting pipe 41 on the lower side of the last tubular membrane module 39 passed through, and flows into the water storage chamber 7 from the discharge pipe 42, and finally flows out of the tank body 1 through the outlet pipe 9.

[0085] It should be noted that, in this article, relational terms such as first and second, etc. are only used to distinguish one entity or operation from another entity or operation, and do not necessarily require or imply any such actual relationship or order between these entities or operations. Moreover, the terms "include", "comprises" or any other variations thereof are intended to cover non-exclusive inclusion, so that a process, method, article or device including a series of elements includes not only those elements, but also other elements not explicitly listed, or also includes elements inherent to such process, method, article or device.

[0086] Finally, it should be noted that the above description is only a preferred embodiment of the present invention and is not intended to limit the present invention. Although the present invention has been described in detail with reference to the aforementioned embodiments, those skilled in the art can still modify the technical solutions described in the aforementioned embodiments or replace some of the technical features therein by equivalents. Any modification, equivalent replacement, improvement, etc. made within the spirit and principle of the present invention shall be included in the protection scope of the present invention.

Claims

1. A seawater pollution purification device, characterized in that: The invention comprises a tank body (1), wherein a cavity is formed in the tank body (1), a cylinder body 1 (3) is sleeved in the tank body (1), a cylinder body 2 (4) is sleeved in the cylinder body 1 (3), both ends of the cylinder body 1 (3) and the cylinder body 2 (4) along the axial direction are sealed with the inner wall of the cavity, a reaction chamber (5) is formed between the cylinder body 1 (3) and the inner wall of the cavity, a filtering chamber (6) is formed between the inner wall of the cylinder body 1 (3) and the outer wall of the cylinder body 2 (4), a water storage chamber (7) is formed between the inner wall of the cylinder body 2 (4) and the inner wall of the cavity, and a stirring assembly (16) is arranged in the reaction chamber (5); The stirring assembly (16) comprises a fixing ring (17), the fixing ring (17) being provided with a plurality of through holes (18), a plurality of layers of catalyst reaction plates (22) being arranged on the upper side of the fixing ring (17), a plurality of connecting rods (23) being fixedly connected to the upper and lower sides of each layer of the catalyst reaction plates (22), two hinge rods (24) being hingedly connected to the two ends of the connecting rods (23) along the axial direction, the two hinge rods (24) corresponding to the catalyst reaction plates (22) of the upper and lower layers adjacent to each other being hingedly connected, the lower ends of the two hinge rods (24) on the catalyst reaction plate (22) of the lowermost layer being hingedly connected to the fixing ring (17), the upper sides of the two hinge rods (24) on the catalyst reaction plate (22) of the uppermost layer being hingedly connected to a connecting ring (25), and a plurality of electric telescopic rods (26) being fixedly connected to the side of the connecting ring (25) away from the catalyst reaction plate (22); A plurality of groups of annular air pipes (10) are arranged along the axial direction on the circumferential side of the inner wall of the cylinder body (3); a plurality of exhaust pipes (11) are fixedly connected to the outer circumferential side of the annular air pipes (10); the exhaust pipes (11) extend through the cylinder wall of the cylinder body (3) away from the annular air pipes (10) and are connected to the reaction chamber (5) for introducing ozone into the reaction chamber (5).

2. A seawater pollution purification device according to claim 1, characterized in that: A plurality of inlet ports (37) are provided on the upper side of the cylinder body (3), and a filter tube (38) is provided in the filter chamber (6) corresponding to the inlet ports (37), and an input port of the filter tube (38) is connected to the inlet port (37); A plurality of tubular membrane assemblies (39) are sleeved in the filter tube (38), and an electric control valve (40) is fixedly connected to the upper side of each tubular membrane assembly (39) on the filter tube (38). The upper side of each group of electric control valves (40) and the lower side of the lowest tubular membrane assembly (39) on the filter tube (38) are connected to a connecting pipe (41), and the side of each connecting pipe (41) away from the filter tube (38) passes through the wall of the second cylinder body (4) and is fixedly connected to a discharge pipe (42). Each connecting pipe (41) is fixedly connected to the second electric control valve (43), and the discharge pipe (42) is located in the water storage chamber (7).

3. A seawater pollution purification device according to claim 2, characterized in that: The fixing ring (17) is arranged concentrically with the reaction chamber (5), the inner ring wall and the outer ring wall of the fixing ring (17) are fixedly connected to the outer wall of the cylinder body (3) and the inner wall of the tank body (1) respectively, and the fixing ring (17) is located on the upper side of the uppermost group of annular air pipes (10); A plurality of the through holes (18) are evenly distributed in a circle with the axis of the fixing ring (17) as the center, and a waterproof motor (19) is arranged in each of the through holes (18). A connecting frame (20) is sleeved on the outer side of the waterproof motor (19), and a side of the connecting frame (20) away from the waterproof motor (19) is fixedly connected to the inner wall of the through hole (18), and a stirring blade (21) is fixedly connected to the output end of the waterproof motor (19).

4. A seawater pollution purification device according to claim 3, characterized in that: The lower side of the tank body (1) is fixedly connected to a water inlet pipe (8) and a water outlet pipe (9), the output end of the water inlet pipe (8) is in communication with the reaction chamber (5), the input end of the water outlet pipe (9) is in communication with the water storage chamber (7), and the water inlet pipe (8) is fixedly connected to a sampler, an online pH detector and a flow control valve.

5. A seawater pollution purification device according to claim 4, characterized in that: A plurality of groups of annular air pipes (10) are linearly arranged along the axial direction of the cylinder body (3); a plurality of exhaust pipes (11) are evenly distributed in a circle with the axis of the annular air pipe (10) as the center; each exhaust pipe (11) is fixedly connected to a one-way air valve; the input end of each group of annular air pipes (10) is connected to an air intake branch pipe (12); each air intake branch pipe (12) is fixedly connected to a control valve; the input end of each air intake branch pipe (12) is commonly connected to an air intake pipe (13); the input end of the air intake pipe (13) passes through the tank body (1) and is fixedly connected to an air pump (14); the input end pipeline of the air pump (14) is connected to an ozone generator (15).

6. A seawater pollution purification device according to claim 5, characterized in that: An annular water pipe (27) and an annular liquid pipe (28) are arranged below the lowest group of annular air pipes (10) in the filter chamber (6).

7. A seawater pollution purification device according to claim 6, characterized in that: A plurality of drainage pipes (29) are fixedly connected to the outer circumference of the annular water pipe (27). The plurality of drainage pipes (29) are evenly distributed around the circumference of the annular water pipe (27) with the axis of the annular water pipe (27) as the center. The drainage pipes (29) are connected to the tube cavity of the annular water pipe (27). The side of the drainage pipe (29) away from the annular water pipe (27) penetrates the wall of the cylinder body (3) to connect to the reaction chamber (5). Each drainage pipe (29) is fixedly connected to a one-way valve (1), and the one-way valve (1) is located in the filter chamber (6); The input end of the annular water pipe (27) is connected to a liquid inlet pipe (30), the input end of the liquid inlet pipe (30) passes through the tank body (1) and is fixedly connected to a liquid pump (31), the input end pipeline of the liquid pump (31) is connected to a water tank (32), the water tank (32) contains hydrogen peroxide, and the pipeline connecting the liquid pump (31) to the water tank (32) is fixedly connected to a flow control valve (2).

8. A seawater pollution purification device according to claim 7, characterized in that: A plurality of drainage pipes (33) are fixedly connected to the outer circumferential side of the annular liquid pipe (28), and the plurality of drainage pipes (33) are evenly distributed in a circle with the axis of the annular liquid pipe (28) as the center. The drainage pipes (33) are connected to the tube cavity of the annular liquid pipe (28), and the side of the drainage pipe (33) away from the annular liquid pipe (28) penetrates the wall of the cylinder body (3) to connect to the reaction chamber (5). Each of the drainage pipes (33) is fixedly connected to a second one-way valve, and the second one-way valve is located in the filter chamber (6); The input end of the annular liquid pipe (28) is connected to two second liquid inlet pipes (34), and the input end of each second liquid inlet pipe (34) passes through the tank body (1) and is fixedly connected to a second liquid pump (35). The input ends of the two second liquid pumps (35) are respectively connected to two liquid tanks (36) by pipelines. The two liquid tanks (36) contain an acid solution and an alkaline solution respectively. The pipelines connecting the two second liquid pumps (35) to the liquid tanks (36) are both fixedly connected to a flow control valve (3).

9. A method for purifying seawater pollution by a purification device, which is implemented based on the seawater pollution purification device of claim 8, characterized in that: S1: sampling and testing the seawater in the water inlet pipe (8) by using a sampler, testing the pH value of the seawater in the water inlet pipe (8) by using a pH online detector, and determining the content of antibiotics in the seawater and the pH value of the seawater; S2: According to the content of antibiotics in the seawater, a certain volume of ozone is introduced from bottom to top through a corresponding number of annular air pipes (10) to allow the ozone to enter the reaction chamber (5), a certain volume of hydrogen peroxide is introduced into the reaction chamber (5) through an annular water pipe (27), and an acidic solution or an alkaline solution is introduced into the reaction chamber (5) through an annular liquid pipe (28) to maintain the pH value of the seawater at a pH value of A1; S3: mixing and stirring the seawater, ozone and hydrogen peroxide through a stirring assembly (16), and driving the seawater to flow upward; S4: controlling the output end of the electric telescopic rod (26) to control a corresponding number of catalyst reaction plates (22) to be compressed and moved below the inlet (37) to participate in the reaction between ozone and antibiotic components in seawater; S5: After the reaction is completed, the seawater flows into the filter tube (38), and is sampled again by the second sampler, and the antibiotic content in the seawater after the reaction is sampled again for detection, so as to determine the antibiotic content in the seawater after the reaction; S6: According to the content of antibiotics in the seawater after the reaction, a corresponding number of electric control valves 1 (40) and electric control valves 2 (43) are closed from bottom to top, so that the seawater passes through a corresponding number of tubular membrane modules (39) for filtration, flows into the discharge pipe (42) from the connecting pipe (41) at the lower side of the last tubular membrane module (39) passed through, and flows into the water storage chamber (7) from the discharge pipe (42), and finally flows out of the tank body (1) through the outlet pipe (9).

Citation Information

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