Fluorescence scanning coupled with electrodialysis optimized electro-Fenton wastewater treatment combination device

By optimizing the combined electro-Fenton wastewater treatment device using fluorescence scanning coupled with electrodialysis, the concentration of Cl- can be precisely analyzed and controlled. This solves the problems of low efficiency and high cost of Fe2+/HClO-type electro-Fenton reactions in the treatment of high-salt organic wastewater, achieving efficient and low-cost wastewater treatment.

CN121044781BActive Publication Date: 2026-01-30NORTHEAST INST OF GEOGRAPHY & AGRIECOLOGY C A S
View PDF 6 Cites 0 Cited by

Patent Information

Application Number
CN202511604738.3
Authority / Receiving Office
CN · China
Patent Type
Patents(China)
Current Assignee / Owner
Filing Date
2025-11-05
Publication Date
2026-01-30
Estimated Expiration
2045-11-05

AI Technical Summary

Technical Problem

Existing technologies cannot effectively utilize Cl- in high-salt wastewater to promote the efficient and safe operation of Fe2+/HClO-type electro-Fenton reactors, resulting in high costs and poor effectiveness in treating high-salt organic wastewater.

Method used

An optimized electro-Fenton wastewater treatment device using fluorescence scanning coupled with electrodialysis is employed. The fluorescence scanning module and the humification index calculation module accurately analyze the Cl- concentration. Combined with the electrodialysis Cl- removal device, the Cl- concentration is scientifically controlled to provide suitable conditions for Fe2+/HClO-type electro-Fenton reactions and to achieve the prior utilization and subsequent removal of salts.

Benefits of technology

It has achieved low-cost, high-efficiency, and full-indicator compliance discharge of high-salt organic wastewater, improved wastewater treatment efficiency and quality, reduced treatment costs, and promoted the sustainable use of resources.

✦ Generated by Eureka AI based on patent content.

Smart Images

  • Figure CN121044781B_ABST
    Figure CN121044781B_ABST
Patent Text Reader

Abstract

This invention discloses a fluorescence scanning coupled with electrodialysis optimized electro-Fenton wastewater treatment combined device, relating to the field of wastewater treatment. It includes a pretreatment system, an analysis system, and a treatment system. This fluorescence scanning coupled with electrodialysis optimized electro-Fenton wastewater treatment combined device uses a fluorescence scanning module to perform fluorescence scanning on the wastewater in the pretreatment tank and transmits the data to a humification index calculation module to accurately analyze and determine suitable Cl levels. ‑ Concentration. Electrodialysis for Cl removal. ‑ The device is based on Cl ‑ Based on the results of the concentration sensor feedback and calculation module, the Cl in wastewater is scientifically controlled. ‑ Concentration, for Fe 2+ The HClO-type electro-Fenton reactor creates conditions for efficient and safe operation, promoting its effective treatment of organic matter. Simultaneously, the device utilizes salts before removal, avoiding resource waste. Ultimately, it achieves full compliance with discharge standards for high-salt organic wastewater at low cost, not only improving wastewater treatment efficiency and quality but also reducing treatment costs, which is of great significance for environmental protection and sustainable resource utilization.
Need to check novelty before this filing date? Find Prior Art

Description

Technical Field

[0001] This invention relates to wastewater treatment technology, specifically to a fluorescent scanning coupled electrodialysis optimized electro-Fenton wastewater treatment combination device. Background Technology

[0002] High-salt organic wastewater, such as pharmaceutical wastewater, saline-alkali land remediation wastewater, and landfill leachate, not only contains a large amount of salt (Cl... - SO4 2- Ca 2+ Na + High-salinity organic wastewater contains a variety of pollutants, including plasma and various organic pollutants, some of which even contain oils and toxic heavy metal ions. Direct discharge without treatment can cause serious pollution to soil, surface water, and groundwater. Recalcitrant organic matter is the main pollutant in high-salinity organic wastewater. Treatment methods such as flotation, evaporation, solidification, and coagulation only transfer recalcitrant organic matter, not remove the pollutants. In contrast, electrochemical oxidation utilizes the highly oxidizing active components in the solution to degrade organic matter into small-molecule intermediates or directly mineralize it. It offers advantages such as short reaction time, thorough oxidation, and ease of automation, making it a promising candidate for high-salinity organic wastewater treatment.

[0003] Electro-Fenton reactors efficiently degrade organic matter by generating highly oxidizing free radicals (•OH), making them a highly efficient method for treating organic wastewater. Continuous O2 exposure is both a necessary condition for the operation of an electro-Fenton reactor and a major source of operating costs. 2+ The HClO-based electro-Fenton method utilizes Cl- in high-salt wastewater to oxidize Cl- at the anolyse into the substrate HClO, which is then reduced at the cathode to produce Fe. 2+ The reaction produces oxide species Fe IV O 2+ It degrades organic pollutants, avoids exposure to O2, and has significant cost advantages.

[0004] Patent CN107540135B discloses a safe and efficient combined process for treating concentrated nanofiltration leachate from landfills. This process removes organic pollutants and toxic byproducts through three steps: iron-based flocculation and sedimentation, electro-Fenton-like advanced oxidation, and activated carbon adsorption. Patent CN115745097A discloses a dual-electro-Fenton treatment device for high-salt organic wastewater, integrating a water quality and quantity adjustment system, a pH adjustment system, a dual-electro-Fenton reaction system, and a mixing system. This solves the problem of treating high-salt organic wastewater with Cl-... − The oxidation to active chlorine leads to a decrease in the degradation efficiency of organic matter, and this is addressed by running Fe... 2+ / HClO-based electro-Fenton converters have enabled the utilization of active chlorine. Patent CN112679559A discloses a method for separating and purifying xylose using electrodialysis combined with flocculation technology. This method utilizes bipolar membrane electrodialysis to recover high-purity inorganic acids while simultaneously raising the pH to near the isoelectric point of the xylose hydrolysate colloidal system. Flocculants are added to enhance the destabilization and precipitation of large molecules such as colloids, thus achieving green and efficient purification of the xylose hydrolysate. Patent CN117185436A describes an electrodialysis-three-dimensional electrode reaction method for simultaneous desalination and pollution reduction of high-salt landfill leachate. This method uses magnetic nitrogen-doped biochar granular electrode materials, placed in the concentration chamber of an electrodialysis reaction tank to construct a three-dimensional electrode reaction system, with the granular electrodes suspended by aeration. These works have promoted the application and development of electrochemical oxidation in the treatment of high-salt organic wastewater, but they also have limitations in analyzing Cl... − Effects on Fe 2+ There has been little attention paid to the electro-Fenton operation of HClO-type compounds, and even less attention has been paid to regulating Cl... − Technologies to improve the efficiency of simultaneous removal of organic pollutants and salinity from high-salinity organic wastewater and related technologies to ensure effluent safety. Summary of the Invention

[0005] The purpose of this invention is to provide a fluorescence scanning coupled with electrodialysis optimized electro-Fenton wastewater treatment combination device to solve the problem that existing technologies cannot utilize Cl in high-salt wastewater. - Promote Fe 2+ The HClO-type electro-Fenton reactor operates efficiently and safely, enabling it to achieve low-cost, high-efficiency, and fully compliant discharge of high-salt organic wastewater.

[0006] To achieve the above objectives, the present invention provides the following technical solution: a fluorescence scanning coupled electrodialysis optimized electro-Fenton wastewater treatment combined device, comprising a pretreatment system, an analysis system, and a treatment system. The pretreatment system includes a mounting plate, on which a wastewater tank is fixedly connected. A first bidirectional pump is fixedly connected to the wastewater tank via a pipeline, and the output end of the first bidirectional pump is fixedly connected to a pretreatment tank via a pipeline.

[0007] The analysis system includes a fluorescence scanning module, a humification index calculation module, and a Cl... - A concentration sensor is included, and the fluorescence scanning module is mounted on the pretreatment tank. The fluorescence scanning module is electrically connected to the humification index calculation module.

[0008] The processing system includes a Cl that is fixedly connected to the mounting plate. - Treatment tanks and organic matter treatment tanks, wherein Cl - A feed pipe is fixedly connected to the bottom of the treatment tank. A second bidirectional pump is installed on the feed pipe. A connecting pipe is fixedly connected to one end of the feed pipe, and an inlet pipe fixedly connected to the connecting pipe is rotatably connected to the inlet pipe, which is fixedly connected to the organic matter treatment tank. -The treatment tank is equipped with electrodialysis for Cl removal. - The device, the Cl - The processing tank is equipped with Cl - Concentration sensor, Fe is installed on the organic matter treatment tank. 2+ / HClO type electro-Fenton reactor, wherein Cl - One side of the treatment tank is connected to the wastewater pool via pipes and a water pump. The humification index calculation module is connected to the Fe... 2+ The HClO-type electro-Fenton reactor is electrically connected, and the Cl... - Concentration sensor and electrodialysis dechlorination - The device is electrically connected.

[0009] Furthermore, a connecting frame is fixedly connected to the outer surface of the feed pipe, and a scraper is fixedly connected to the outer surface of the connecting frame. A transmission mechanism connected to the organic matter treatment tank is driven to the outer surface of the feed pipe. The transmission mechanism is used to drive the feed pipe to rotate. A first discharge pipe is fixedly connected to the outer surface of the connecting pipe. An electromagnetic valve is installed on the first discharge pipe. An electromagnetic valve is installed on the feed pipe. A sediment purification mechanism connected to the mounting plate is fixedly connected to one end of the first discharge pipe. The sediment purification mechanism is used to purify Fe in the organic matter treatment tank. 2+ The precipitate in the water after purification by the HClO-type electro-Fenton reactor is further purified. The precipitate purification mechanism is connected to the Cl... - The processing tank is connected.

[0010] Furthermore, the sediment purification and treatment mechanism includes a first treatment box fixedly connected to a mounting plate. A first rotation drive is fixedly connected to one side of the first treatment box. A purification plate rotatably connected to the first treatment box is fixedly connected to the output end of the first rotation drive. Multiple baffles are fixedly connected to the top and bottom of the purification plate. Connecting mechanisms are provided on both sides of the purification plate. A second drain pipe is fixedly connected to the first treatment box. The second drain pipe is connected to the connecting mechanisms. The connecting mechanisms are used to supply the filtered water blocked on the purification plate into the second drain pipe. One end of the second drain pipe is fixedly connected to a second treatment box fixedly connected to the mounting plate. One side of the second treatment box is connected to Cl via a pipe and a water pump. - The treatment tank is connected.

[0011] Furthermore, a first filter screen is fixedly connected inside the second processing box, a second filter screen is fixedly connected to the second processing box below the first filter screen, and a third filter screen is fixedly connected to the second processing box below the second filter screen.

[0012] Furthermore, the connecting mechanism includes a water inlet groove on the purification plate, a third drain pipe slidably connected in the water inlet groove, a spring fixedly connected to the water inlet groove via a connecting block on the outer surface of the third drain pipe, a connecting iron ring fixedly connected to one side of the third drain pipe, an electromagnet block fixedly connected to the outer surface of the first treatment box, and a water baffle plate fixedly connected to the surface of the purification plate.

[0013] Furthermore, a cleaning plate is slidably connected to one side of the first processing box, a cleaning brush is fixedly connected to one side of the cleaning plate, and a drive mechanism connected to the first processing box is fixedly connected to one side of the cleaning plate. The drive mechanism is used to drive the cleaning plate to reciprocate.

[0014] Furthermore, the driving mechanism includes a transmission column fixedly connected to the cleaning plate, the transmission column being slidably connected to the first processing box, and one end of the transmission column being fixedly connected to a telescopic driving member fixedly connected to the first processing box via a connecting plate.

[0015] Furthermore, the transmission mechanism includes a second rotation drive component fixedly connected to the organic matter processing tank. The output end of the second rotation drive component is fixedly connected to a transmission shaft. A first gear is fixedly sleeved on the outer surface of the transmission shaft. A second gear fixedly sleeved on the outer surface of the first gear is meshed with the outer surface of the first gear.

[0016] Furthermore, a cleaning door is rotatably connected to the bottom of the first processing box.

[0017] Furthermore, the Cl - A drain pump is fixedly connected to the bottom of the treatment tank via a pipe.

[0018] Compared with existing technologies, the fluorescence scanning coupled electrodialysis optimized electro-Fenton wastewater treatment combined device provided by the present invention has the following beneficial effects:

[0019] (1) The wastewater in the pretreatment tank was scanned by a fluorescence scanning module, and the data was transmitted to the humification index calculation module to accurately analyze the appropriate Cl. - Concentration. Electrodialysis for Cl removal. - The device is based on Cl - Based on the results of the concentration sensor feedback and calculation module, the Cl in wastewater is scientifically controlled. - Concentration, for Fe 2+ The HClO-type electro-Fenton reactor creates conditions for efficient and safe operation, promoting its effective treatment of organic matter. Simultaneously, the device utilizes salts before removal, avoiding resource waste. Ultimately, it achieves full compliance with discharge standards for high-salt organic wastewater at low cost, not only improving wastewater treatment efficiency and quality but also reducing treatment costs, which is of great significance for environmental protection and sustainable resource utilization.

[0020] (2) This device can effectively filter and clean the sediment in the treated wastewater. By closing the solenoid valve of the feed pipe and opening the solenoid valve of the first discharge pipe, the wastewater enters the first treatment tank and falls evenly onto the purification plate through the horizontal pipe and the drain hole. The transmission mechanism drives the feed pipe to rotate, and the scraper cleans the sediment on the inner wall of the organic matter treatment tank, reducing the difficulty of discharge. The baffle plate on the purification plate first blocks the larger sediments, and the filtered water enters the second treatment tank through the inlet tank, the third drain pipe and the second drain pipe, and then the smaller sediments are filtered layer by layer by the three-layer filter screen. This staged filtration method effectively prevents the subsequent filter screen from clogging quickly, improves the service life and filtration stability of the filtration device, and can comprehensively and efficiently remove sediments from the wastewater, ensuring the quality of wastewater treatment.

[0021] (3) This device achieves automated cleaning of the purification plate, improving the purification effect and service life. When the purification plate filters for a period of time and there are many impurities on the baffle plate, the first rotating drive component drives the purification plate to rotate counterclockwise. Before rotation, the electromagnet block is de-energized to prevent obstruction of rotation. After rotation, the electromagnet block is energized again to connect to another third drain pipe, and the other side of the purification plate continues to purify and filter. At the same time, the telescopic drive component drives the cleaning plate and cleaning brush to move back and forth, automatically cleaning the sediment on the purification plate and baffle plate. This automated cleaning design eliminates the need for frequent manual operation, reduces labor costs, and can clean impurities in a timely manner, avoiding the accumulation of impurities that affects the purification effect, effectively extending the service life of the purification device and ensuring long-term stable operation of the device. Attached Figure Description

[0022] To more clearly illustrate the technical solutions in the embodiments of this application or the prior art, the drawings used in the embodiments will be briefly introduced below. Obviously, the drawings described below are only some embodiments recorded in this invention. For those skilled in the art, other drawings can be obtained based on these drawings.

[0023] Figure 1 This is a first perspective view of the external structure of the present invention;

[0024] Figure 2 This is a second perspective view of the external structure of the present invention;

[0025] Figure 3 This is a side view of the internal structure of the present invention;

[0026] Figure 4 For the present invention Figure 2 Enlarged view of A in the middle;

[0027] Figure 5 For the present invention Figure 3 A magnified view of B in the middle.

[0028] Explanation of reference numerals in the attached figures:

[0029] 1. Mounting plate; 2. Wastewater tank; 3. First bidirectional pump; 4. Pretreatment tank; 5. Fluorescence scanning module; 6. Humic index calculation module; 7. Cl - Concentration sensor; 8. Cl - 9. Processing tank; 10. Organic matter processing tank; 11. Feed pipe; 12. Second bidirectional pump; 13. Connecting pipe; 14. Feed pipe; 15. Electrodialysis dechlorination system - Apparatus; 15, Fe 2+ / HClO-type electro-Fenton reactor; 21. Connecting frame; 22. Scraper; 23. First discharge pipe; 31. First processing box; 32. First rotation drive component; 33. Purification plate; 34. Baffle plate; 35. Second drain pipe; 36. Second processing box; 41. First filter screen; 42. Second filter screen; 43. Third filter screen; 51. Water inlet tank; 52. Third drain pipe; 53. Spring; 54. Connecting iron ring; 55. Electromagnet block; 56. Water baffle plate; 61. Cleaning plate; 62. Cleaning brush; 63. Transmission column; 64. Telescopic drive component; 71. Second rotation drive component; 72. Transmission shaft; 73. First gear; 74. Second gear. Detailed Implementation

[0030] To enable those skilled in the art to better understand the technical solution of the present invention, the present invention will be further described in detail below with reference to the accompanying drawings.

[0031] Example 1

[0032] Please see Figures 1 to 5 As shown, the present invention provides a fluorescent scanning coupled electrodialysis optimized electro-Fenton wastewater treatment combined device, including a pretreatment system, an analysis system and a treatment system. The pretreatment system includes a mounting plate 1, a wastewater tank 2 fixedly connected to the mounting plate 1, a first bidirectional pump 3 fixedly connected to the wastewater tank 2 through a pipe, and a pretreatment tank 4 fixedly connected to the output end of the first bidirectional pump 3 through a pipe.

[0033] The analysis system includes a fluorescence scanning module 5, a humification index calculation module 6, and a Cl... - Concentration sensor 7 and fluorescence scanning module 5 are installed on pretreatment tank 4. Fluorescence scanning module 5 is electrically connected to humification index calculation module 6.

[0034] The processing system includes Cl, which is fixedly connected to the mounting plate 1. - Treatment tank 8 and organic matter treatment tank 9, Cl -A feed pipe 10 is fixedly connected to the bottom of the treatment tank 8. A second bidirectional pump 11 is installed on the feed pipe 10. A connecting pipe 12 is fixedly connected to one end of the feed pipe 10. One end of the connecting pipe 12 is rotatably connected to an inlet pipe 13 that is fixedly connected to the organic matter treatment tank 9. - The treatment tank 8 is equipped with an electrodialysis dechlorination system. - Apparatus 14, Cl - The processing tank 8 is equipped with Cl - Concentration sensor 7, organic matter treatment tank 9 is equipped with Fe 2+ / HClO-type electro-Fenton reaction apparatus 15, Cl - One side of the treatment tank 8 is connected to the wastewater pool 2 via pipes and a water pump. The humification index calculation module 6 and Fe... 2+ / HClO type electro-Fenton reaction apparatus 15 electrical connection, Cl - Concentration sensor 7 and electrodialysis Cl removal - Device 14 is electrically connected, Cl - A drain pump is fixedly connected to the bottom of treatment tank 8 via a pipe.

[0035] Wastewater from wastewater tank 2 is quantitatively transported to pretreatment tank 4 via a first bidirectional pump 3 and pipeline. Then, fluorescence scanning module 5 in pretreatment tank 4 performs fluorescence scanning on the wastewater. The data obtained from fluorescence scanning module 5 is then transmitted to humification index calculation module 6. Subsequently, humification index calculation module 6 analyzes the characteristics of organic matter in the wastewater to determine a suitable Cl- concentration. - After the concentration analysis is completed, the first bidirectional pump 3 returns the wastewater to the wastewater tank 2, and then transports the wastewater to Cl through pumps and pipelines. - In treatment tank 8, then through Cl - Electrodialysis Cl removal in treatment tank 8 - Device 14 for Cl in wastewater - Processing is carried out, and Cl - Cl on processing tank 8 - Concentration sensor 7 monitors Cl in real time - Cl in treatment tank 8 - Concentration, when Cl - The concentration reaches the humification index calculation module 6, which analyzes the characteristics of organic matter in wastewater to determine the appropriate Cl concentration. - At this concentration, electrodialysis removes Cl. - Device 14 stops working, and then Cl is fed through the second bidirectional pump 11, feed pipe 10, connecting pipe 12 and inlet pipe 13. - The wastewater treated in treatment tank 8 is then introduced into organic matter treatment tank 9, where Fe... 2+The HClO-type electro-Fenton reactor 15 starts working to treat the organic matter in the wastewater. After treatment, the wastewater in the organic matter treatment tank 9 is then returned to the Cl-type reactor via the second bidirectional pump 11. - Processing tank 8, then Cl - Electrodialysis for Cl removal in treatment tank 8 - Device 14 for Cl in wastewater - The concentration is reduced to below the emission standard, and then discharged through a drainage pump. The solution is then removed via fluorescence scanning module 5 and electrodialysis for Cl removal. - Device 14 is used to regulate the water quality of high-salt organic wastewater to achieve Cl - Scientific regulation to promote Fe 2+ The HClO-type electro-Fenton reactor aims to achieve efficient and safe operation, prioritizing the utilization and subsequent removal of salts, ultimately enabling low-cost, high-efficiency, and fully compliant discharge of high-salt organic wastewater.

[0036] Example 2

[0037] Based on Example 1, please refer to Figures 1 to 5 As shown, a connecting frame 21 is fixedly connected to the outer surface of the feed pipe 13, and a scraper 22 is fixedly connected to the outer surface of the connecting frame 21. A transmission mechanism connected to the organic matter treatment tank 9 is driven to the outer surface of the feed pipe 13. The transmission mechanism is used to drive the feed pipe 13 to rotate. A first discharge pipe 23 is fixedly connected to the outer surface of the connecting pipe 12. An electromagnetic valve is installed on the first discharge pipe 23. An electromagnetic valve is installed on the feed pipe 10. Then, water enters the first treatment tank 31 through the first discharge pipe 23. A sediment purification mechanism connected to the mounting plate 1 is fixedly connected to one end of the first discharge pipe 23. The sediment purification mechanism is used to purify the sediment in the water after purification by the Fe²⁺ / HClO electro-Fenton reaction device 15 in the organic matter treatment tank 9. The sediment purification mechanism is connected to the Cl⁻ treatment tank 8.

[0038] The sediment purification treatment mechanism includes a first treatment box 31 fixedly connected to the mounting plate 1. A first rotation drive 32, which is a servo motor, is fixedly connected to one side of the first treatment box 31. The servo motor is controlled by a PLC programming program, which can control the servo motor to rotate forward and backward and rotate at different angles. A purification plate 33, which is rotatably connected to the first treatment box 31, is fixedly connected to the output end of the first rotation drive 32. Multiple baffles 34 are fixedly connected to the top and bottom of the purification plate 33. A connecting mechanism is provided on both sides of the purification plate 33. A second drain pipe 35 is fixedly connected to the first treatment box 31. The second drain pipe 35 is connected to the connecting mechanism, which is used to supply the filtered water blocked on the purification plate 33 into the second drain pipe 35. One end of the second drain pipe 35 is fixedly connected to a second treatment box 36 fixedly connected to the mounting plate 1. One side of the second treatment box 36 is connected to the Cl⁻ treatment tank 8 through a pipe and a water pump.

[0039] A first filter plate 41 is fixedly connected inside the second processing box 36. A second filter plate 42, which is fixedly connected to the second processing box 36, is provided below the first filter plate 41. A third filter plate 43, which is fixedly connected to the second processing box 36, is provided below the second filter plate 42.

[0040] The connecting mechanism includes a water inlet trough 51 opened on the purification plate 33, a third drain pipe 52 slidably connected in the water inlet trough 51, a spring 53 fixedly connected to the water inlet trough 51 via a connecting block on the outer surface of the third drain pipe 52, a connecting iron ring 54 fixedly connected to one side of the third drain pipe 52, an electromagnet block 55 fixedly connected to the outer surface of the first treatment box 31, and a water baffle plate 56 fixedly connected to the surface of the purification plate 33.

[0041] A cleaning plate 61 is slidably connected to one side of the first processing box 31. A cleaning brush 62 is fixedly connected to one side of the cleaning plate 61. A drive mechanism connected to the first processing box 31 is fixedly connected to one side of the cleaning plate 61. The drive mechanism is used to drive the cleaning plate 61 to reciprocate.

[0042] The drive mechanism includes a transmission column 63 fixedly connected to the cleaning plate 61, the transmission column 63 being slidably connected to the first processing box 31, and one end of the transmission column 63 being fixedly connected to a telescopic drive member 64 fixedly connected to the first processing box 31 via a connecting plate.

[0043] The transmission mechanism includes a second rotation drive 71 fixedly connected to the organic matter processing tank 9. The second rotation drive 71 is a servo motor, which is controlled by a PLC programming program. The servo motor can be controlled to rotate forward and backward and rotate at different angles. A transmission shaft 72 is fixedly connected to the output end of the second rotation drive 71. A first gear 73 is fixedly sleeved on the outer surface of the transmission shaft 72. A second gear 74 is meshed with the outer surface of the first gear 73 and fixedly sleeved on the feed pipe 13. The second rotation drive 71 drives the transmission shaft 72 to rotate, and the transmission shaft 72 drives the feed pipe 13 to rotate through the first gear 73 and the second gear 74.

[0044] A cleaning door is rotatably connected to the bottom of the first processing box 31.

[0045] When Fe in organic matter treatment tank 9 2+ When precipitates form in the wastewater treated by the HClO-type electro-Fenton reactor 15, the solenoid valve on the feed pipe 10 is closed, and the solenoid valve on the first discharge pipe 23 is opened. Water then enters the first treatment tank 31 through the first discharge pipe 23. The first discharge pipe 23 evenly distributes water onto the purification plate 33 through a horizontal pipe and its drainage holes. During drainage, the transmission mechanism simultaneously rotates the feed pipe 13, which in turn rotates the connecting frame 21. The connecting frame 21 then rotates the scraper 22, which cleans the precipitates adhering to the inner wall of the organic matter treatment tank 9 and lowers the tank, facilitating discharge from the feed pipe 13. Simultaneously, the electromagnet block 55 on the first treatment tank 31 is activated. The electromagnet block 55 generates magnetic force that attracts the connecting iron ring 54 on the third drain pipe 52, thus fixing the third drain pipe 52 to the second drain pipe 35. The water then enters the purification tank. Wastewater on plate 33 is blocked by multiple baffles 34 on the purification plate 33. At this time, the baffles 34 block larger sediments in the wastewater, achieving sufficient filtration of larger sediments. Then, the filtered water enters the third drain pipe 52 through the water inlet 51 on the purification plate 33. Then, the third drain pipe 52 enters the second treatment tank 36 through the second drain pipe 35. Then, the first filter plate 41, the second filter plate 42, and the third filter plate 43 in the second treatment tank 36 filter the wastewater layer by layer, achieving the filtration of smaller sediments in the wastewater. This achieves sufficient filtration and cleaning of sediments in the treated wastewater. At the same time, the multiple baffles 34 on the purification plate 33 filter larger sediments, effectively preventing rapid clogging of subsequent filter plates, improving the service life and stability of the filtration device. Finally, the filtered and cleaned wastewater is pumped into the Cl⁻ treatment tank 8 through pipes and a water pump for further treatment.

[0046] During the filtration process of the purification plate 33, after a period of filtration, when there are many impurities filtered on the baffle plate 34, the first rotating drive 32 drives the purification plate 33 to rotate counterclockwise. Before rotation, the electromagnet block 55 is de-energized, causing the third drain pipe 52 to retract under the force of the spring 53, preventing obstruction of the rotation of the purification plate 33. Then, the filter surface of the purification plate 33 that was just filtered rotates to the bottom. At this time, the electromagnet block 55 is energized again, attracting and connecting the other third drain pipe 52. At the same time, the purification plate 33 continues to purify and filter through the baffle plate 34 on the other side. Then, the telescopic drive 64 drives the connecting plate and the transmission column 63 to move back and forth. The transmission column 63 drives the cleaning plate 61 and the cleaning brush 62 to move back and forth. The cleaning brush 62 automatically cleans the sediment on the purification plate 33 and the baffle plate 34, thereby realizing the automated cleaning of the purification plate 33 and improving the purification effect and service life of the purification device.

[0047] Working principle: Wastewater from wastewater tank 2 is quantitatively transported to pretreatment tank 4 via a first bidirectional pump 3 and pipeline. Then, fluorescence scanning module 5 in pretreatment tank 4 performs fluorescence scanning on the wastewater. The data obtained from fluorescence scanning module 5 is then transmitted to humification index calculation module 6. Subsequently, humification index calculation module 6 analyzes the characteristics of organic matter in the wastewater to determine a suitable Cl- concentration. - After the concentration analysis is completed, the first bidirectional pump 3 returns the wastewater to the wastewater tank 2, and then transports the wastewater to Cl through pumps and pipelines. - In treatment tank 8, then through Cl - Electrodialysis Cl removal in treatment tank 8 - Device 14 for Cl in wastewater - Processing is carried out, and Cl - Cl on processing tank 8 - Concentration sensor 7 monitors Cl in real time - Cl in treatment tank 8 - Concentration, when Cl - The concentration reaches the humification index calculation module 6, which analyzes the characteristics of organic matter in wastewater to determine the appropriate Cl concentration. - At this concentration, electrodialysis removes Cl. - Device 14 stops working, and then Cl is fed through the second bidirectional pump 11, feed pipe 10, connecting pipe 12 and inlet pipe 13. - The wastewater treated in treatment tank 8 is then introduced into organic matter treatment tank 9, where Fe... 2+ The HClO-type electro-Fenton reactor 15 starts working to treat the organic matter in the wastewater. After treatment, the wastewater in the organic matter treatment tank 9 is then returned to the Cl-type reactor via the second bidirectional pump 11. - Processing tank 8, then Cl- Electrodialysis for Cl removal in treatment tank 8 - Device 14 for Cl in wastewater - The concentration is reduced to below the emission standard, and then discharged through a drainage pump. The solution is then removed via fluorescence scanning module 5 and electrodialysis for Cl removal. - Device 14 is used to regulate the water quality of high-salt organic wastewater to achieve Cl - Scientific regulation to promote Fe 2+ The HClO-type electro-Fenton reactor aims to achieve efficient and safe operation, prioritizing the utilization and subsequent removal of salts, ultimately enabling low-cost, high-efficiency, and fully compliant discharge of high-salt organic wastewater.

[0048] The foregoing has only described certain exemplary embodiments of the present invention by way of illustration. Undoubtedly, those skilled in the art can modify the described embodiments in various ways without departing from the spirit and scope of the present invention. Therefore, the foregoing drawings and descriptions are illustrative in nature and should not be construed as limiting the scope of protection of the claims of the present invention.

Claims

1. A combination device for fluorescent scanning coupled with electrodialysis for optimizing electro-Fenton-like wastewater treatment, characterized in that Including preprocessing system, analysis system and processing system, preprocessing system includes mounting plate (1), waste water tank (2) is fixedly connected on mounting plate (1), first bidirectional pump (3) is fixedly connected on waste water tank (2) by pipeline, the output end of first bidirectional pump (3) is fixedly connected with pretreatment tank (4) by pipeline; The analysis system comprises a fluorescence scanning module (5), a humification index calculation module (6) and a Cl - concentration sensor (7), the fluorescence scanning module (5) is arranged on a pretreatment tank (4), and the fluorescence scanning module (5) is electrically connected with the humification index calculation module (6); The processing system comprises a Cl - A processing tank (8) and an organic matter processing tank (9), the Cl - A feeding pipe (10) is fixedly connected to the bottom end of the processing tank (8), a second bidirectional pump (11) is arranged on the feeding pipe (10), one end of the feeding pipe (10) is fixedly connected with a connecting pipe (12), one end of the connecting pipe (12) is rotatably connected with a feeding pipe (13) fixedly connected with the organic matter processing tank (9), the Cl - An electrodialysis Cl - Device (14), the Cl - A Cl - A concentration sensor (7), the organic matter processing tank (9) is provided with Fe 2+ / HClO type electro-Fenton reaction device (15), the Cl - One side of the processing tank (8) is connected with a wastewater pool (2) through a pipeline and a water pump, the humification index calculation module (6) is electrically connected with Fe 2+ / HClO type electro-Fenton reaction device (15) is electrically connected, the Cl - The concentration sensor (7) is electrically connected with the electrodialysis Cl - Device (14) is electrically connected.

2. The fluorescence scanning coupled electrodialysis optimization electro-Fenton like wastewater treatment combined device according to claim 1, characterized in that, The outer surface of the feeding pipe (13) is fixedly connected with a connecting frame (21), the outer surface of the connecting frame (21) is fixedly connected with a scraping strip (22), the outer surface of the feeding pipe (13) is drivingly connected with a transmission mechanism connected with the organic matter treatment tank (9), the transmission mechanism is used for driving the feeding pipe (13) to rotate, the outer surface of the connecting pipe (12) is fixedly connected with a first discharging pipe (23), the first discharging pipe (23) is provided with a solenoid valve, the feeding pipe (10) is provided with a solenoid valve, one end of the first discharging pipe (23) is fixedly connected with a sediment purification mechanism connected with the mounting plate (1), the sediment purification mechanism is used for purifying Fe 2+ The sediment purification mechanism is connected with the Cl - Treatment tank (8).

3. The Fluorescence Scanning Coupled with Electrodialysis Optimized Electro-Fenton-like Wastewater Treatment Assembly of claim 2, wherein, The precipitate purification treatment mechanism comprises a first treatment box (31) fixedly connected with the mounting plate (1), one side of the first treatment box (31) is fixedly connected with a first rotating driving element (32), the output end of the first rotating driving element (32) is fixedly connected with a purification plate (33) rotatably connected with the first treatment box (31), the top and the bottom of the purification plate (33) are fixedly connected with a plurality of blocking plates (34), both sides of the purification plate (33) are provided with a connecting mechanism, the first treatment box (31) is fixedly connected with a second drain pipe (35), the second drain pipe (35) is connected with the connecting mechanism, the connecting mechanism is used for supplying the water filtered by the blocking plate (33) into the second drain pipe (35), one end of the second drain pipe (35) is fixedly connected with a second treatment box (36) fixedly connected with the mounting plate (1), one side of the second treatment box (36) is connected with a Cl - The treatment tank (8) is connected.

4. The fluorescence scanning coupled electrodialysis optimization electro-Fenton-like wastewater treatment combined device according to claim 3, characterized in that, The first filter screen plate (41) is fixedly connected in the second treatment box (36), the second filter screen plate (42) is arranged below the first filter screen plate (41) and is fixedly connected with the second treatment box (36), and the third filter screen plate (43) is arranged below the second filter screen plate (42) and is fixedly connected with the second treatment box (36).

5. The fluorescence scanning coupled electrodialysis optimization electro-Fenton like wastewater treatment combined device according to claim 3, characterized in that, The connecting mechanism includes a water inlet groove (51) formed in the purification plate (33), a third drain pipe (52) is slidably connected in the water inlet groove (51), a spring (53) is fixedly connected with the water inlet groove (51) on the outer surface of the third drain pipe (52) through a connecting block, a connecting iron ring (54) is fixedly connected on one side of the third drain pipe (52), an electromagnet block (55) is fixedly connected on the outer surface of the first treatment box (31), and a water blocking frame plate (56) is fixedly connected on the surface of the purification plate (33).

6. The Fluorescence Scanning Coupled with Electrodialysis Optimized Electro-Fenton-like Wastewater Treatment Assembly of claim 3, wherein, One side of the first treatment box (31) is slidably connected with a cleaning plate (61), the cleaning plate (61) is fixedly connected with a cleaning brush (62) on one side, and a driving mechanism connected with the first treatment box (31) is fixedly connected on one side of the cleaning plate (61), so that the cleaning plate (61) can be driven to reciprocate.

7. The Fluorescence Scanning Coupled with Electrodialysis Optimized Electro-Fenton-like Wastewater Treatment Assembly of claim 6, wherein, The driving mechanism includes a transmission column (63) fixedly connected with the cleaning plate (61), the transmission column (63) is slidably connected with the first treatment box (31), and the transmission column (63) is fixedly connected with a telescopic driving piece (64) fixedly connected with the first treatment box (31) on one end through a connecting plate.

8. The Fluorescence Scanning Coupled with Electrodialysis Optimized Electro-Fenton-like Wastewater Treatment Assembly of claim 2, wherein, The transmission mechanism includes a second rotating driving piece (71) fixedly connected with the organic matter treatment tank (9), a transmission shaft (72) fixedly connected with the output end of the second rotating driving piece (71), a first gear (73) fixedly sleeved on the outer surface of the transmission shaft (72), and a second gear (74) fixedly sleeved with the feed pipe (13) and meshingly connected with the outer surface of the first gear (73).

9. The fluorescence scanning coupled electrodialysis optimization electro-Fenton like wastewater treatment combined device according to claim 3, characterized in that, The bottom of the first treatment box (31) is rotatably connected with a cleaning door.

10. The Fluorescence Scanning Coupled with Electrodialysis Optimized Electro-Fenton-like Wastewater Treatment Assembly of claim 2, wherein, The Cl - The bottom of the treatment tank (8) is fixedly connected with a drainage pump through a pipeline.

Citation Information

Patent Citations

  • A safe and efficient combined process for treating landfill leachate nanofiltration concentrate.

    CN107540135B

  • Method for separating and purifying xylose by combining electrodialysis with flocculation technology

    CN112679559A

  • Double electro-Fenton treatment device for high-salt organic wastewater

    CN115745097A

  • Electrodialysis-three-dimensional electrode reaction method for synchronous desalination and pollution reduction of high-salt landfill leachate

    CN117185436A

  • Three-dimensional fluorescence spectrum method for measuring chlorine disinfection by-product precursor in water

    CN101819148A