Treatment device and treatment process for hot spring tail water
By designing a hot spring tail water treatment device, combining multi-layered precipitation, flocculation, oxygen regulation and MBR reactor, the problem of sulfide inhibition in hot spring wastewater treatment is solved, efficient water quality improvement and economic benefits are achieved, and the treated water reaches surface level III is ensured. Class standards.
Patent Information
- Application Number
- CN202411662416.X
- Authority / Receiving Office
- CN · China
- Patent Type
- Applications(China)
- Current Assignee / Owner
- Filing Date
- 2024-11-20
- Publication Date
- 2024-12-31
- Estimated Expiration
- Not applicable · inactive patent
AI Technical Summary
The sulfides in the hot spring wastewater have an inhibitory effect on the biological treatment units of the sewage treatment plant, causing the sewage plant to be paralyzed. The existing technology has insufficient economic benefits and treatment efficiency, making it difficult to effectively treat the hot spring tail water.
A hot spring tail water treatment device is designed, including a regulation unit, a precipitation unit, an oxygen control tank and an MBR reactor. Through multi-layered precipitation, flocculation, oxygen regulation and disinfection treatment, combined with anaerobic, hypoxia and aerobic processes, Use automatic oxygen-controlled and nanofiltration components to ensure that the treated water meets surface level Class III standards.
Effectively prevent blockage, reduce flocculation impurities residues, improve purification accuracy, save floor space, ensure the quality of the treatment water, maintain the qualification of the water in extreme cases, and ensure full disinfection through automatic rush disinfection components.
Smart Images

Figure CN119219273A_ABST
Abstract
Description
Technical Field
[0001] The invention relates to the technical field of wastewater treatment, in particular to a treatment device for hot spring tail water and a treatment process thereof. Background Art
[0002] With the rapid growth of my country's economy, people's living standards have been continuously improved, and the pursuit of quality of life has become higher and higher. Hot spring water is rich in sulfur and other trace elements, which has a good therapeutic effect on skin diseases, rheumatoid arthritis, nerve paralysis, etc. Hot spring baths are also beneficial to blood circulation, promote functional recovery of patients with cerebral thrombosis, and have a significant effect on lowering blood pressure. Therefore, hot spring therapy has gradually entered the public's field of vision and slowly entered daily life.
[0003] The popularity of hot spring therapy has led to a gradual increase in the amount of hot spring wastewater. The sulfide in the hot spring wastewater will have a greater inhibitory effect on the microorganisms in the biological treatment unit of the sewage treatment plant. In severe cases, it will cause the entire sewage treatment plant to be paralyzed, so it must be treated. Considering the seasonality of hot spring therapy and the small proportion of hot spring tailwater in the entire sewage treatment plant, from an economic point of view, it is not economically effective to treat it together with other domestic sewage in the sewage treatment plant. Comprehensive consideration requires that the hot spring tailwater be treated at the front end and in the pollution-producing links such as hot spring hotels and hot spring resorts. After treatment, it can be discharged into the city's inland rivers according to actual conditions, without having to enter the municipal pipe network for re-treatment. Summary of the invention
[0004] The object of the present invention is to provide a hot spring tail water treatment device and a treatment process thereof to solve the problems raised in the prior art.
[0005] To achieve the above object, the present invention provides the following technical solutions:
[0006] The present invention provides a technical solution. The comprehensive treatment pool comprises a regulating unit and a sedimentation unit. The regulating unit is equipped with a submersible flow propeller and two water inlet pumps. The regulating unit is connected with the sedimentation unit, the water inlet pump is connected with the sedimentation unit, a stirring component is arranged in the sedimentation unit, a guide tube is arranged in the sedimentation unit, a sedimentation component is arranged at the bottom of the sedimentation unit, a transfer pump is arranged in the regulating unit, a transfer pipe is arranged at the output end of the transfer pump, the end of the transfer pipe away from the transfer pump is connected with the oxygen control pool, a filter pipe is arranged on the oxygen control pool, the end of the filter pipe away from the oxygen regulating unit is connected with the reaction pool, an MBR reactor is arranged in the reaction pool, a control valve is arranged on the reaction pool, an intermediate water pool is arranged at the end of the control valve away from the reaction pool, a treatment chamber is arranged on the intermediate water pool, a nanofiltration component is arranged in the treatment chamber, a disinfection component is arranged in the intermediate water pool, a discharge pipe is arranged on the intermediate water pool, and the discharge pipe is away from the end of the intermediate water pool. It is connected to the discharge pool. When disinfecting and removing impurities, the hot spring tail water is first sent to the regulating unit. The water inlet pump on the submersible flow propeller will extract the hot spring tail water, and then the hot spring tail water is sent to the sedimentation unit. Then the stirring component will work, and flocculants will be added to the regulating unit at the same time. Then, under the action of the flocculant, the sediment will fall into the sedimentation unit. The filtered water will be sent to the vicinity of the guide tube, and then these hot spring tail waters will enter the oxygen control pool. The oxygen control pool cooperates to control the oxygen content, and then the treated hot spring tail water will be sent to the reaction pool. The MBR reactor can ensure the clarity of the effluent water. According to the comprehensive consideration of the water treatment volume, investment budget and floor area, the appropriate flat membrane or curtain membrane can be selected, and then the reacted hot spring tail water will be sent to the intermediate water pool. The tail water is finally disinfected by the disinfection component and finally discharged in compliance with the standards.
[0007] The sedimentation unit includes a stirring zone and a sedimentation zone. The stirring component is arranged in the stirring zone. The stirring component includes a stirring motor and a stirring frame. A plurality of stirring blades are arranged on the stirring frame. The stirring frame is arranged on the output end of the stirring motor. A drain port is arranged on the sedimentation zone. The drain pipe is connected with the regulating unit. A dosing pipe is arranged in the regulating unit. A dosing device is arranged in the dosing pipe. After the hot spring tail water enters the stirring zone, flocculant is added thereto. Then the stirring motor will drive the stirring frame to rotate. The stirring blades will accelerate the combination of the flocculant and the hot spring tail water. Then the flocculated impurities will enter the sedimentation zone and enter the guide tube. After being extruded and formed by the guide tube, the flocculants can be fully deposited, so that the flocculant can play a full role. Then the flocculants enter the mud discharge component with the water for pressurization. Finally, the mud discharge component will discharge the flocculants from the sedimentation unit, and also reduce the mixing of some smaller flocculants into the subsequent processing operations, so as to improve the purification accuracy. The sedimentation component is waiting to discharge these impurities out of the equipment. Finally, the hot spring tail water with impurities is sent to the drain pipe and enters the regulating unit.
[0008] A sedimentation component is arranged in the sedimentation area, and the sedimentation component includes a polymerization tank. A mud discharge component is arranged in the polymerization tank, and the mud discharge component includes a mud discharge motor and a mud discharge wheel. The mud discharge wheel is arranged on the output end of the mud discharge motor, and the mud discharge motor is arranged in the polymerization tank. A mud discharge auxiliary wheel is arranged in the polymerization tank, and a mud discharge belt is wound around the mud discharge wheel and the mud discharge auxiliary wheel. When the flocculated impurities enter the polymerization tank, the mud discharge motor will drive the mud discharge wheel to rotate, and the mud discharge wheel will drive the mud discharge belt to rotate. The precipitated flocculated impurities will be accumulated in the sedimentation area, waiting to be drained and removed, while avoiding the flocculated impurities clogging the drain pipe and causing the problem of water being unable to discharge.
[0009] A water outlet trough and a squeezing box are provided in the polymerization tank. The water outlet trough is connected to the drain pipe. A squeezing roller and a squeezing motor are provided in the squeezing box. The squeezing roller is arranged on the output end of the squeezing motor. A return water baffle is provided on the squeezing box. A plurality of water flow troughs are provided on the squeezing roller. The return water baffle is in intermittent sliding contact with the squeezing roller. After the flocculants enter the squeezing box, the squeezing motor drives the squeezing roller to rotate, thereby squeezing the impurities and tail water together into the vicinity of the return water baffle. The return water baffle cooperates with the squeezing roller to squeeze and separate the tail water rich in impurities. The squeezed water will flow out from the water flow trough, and the impurities will be sent back to the polymerization tank.
[0010] An oxygen supply system is arranged in the oxygen regulating unit, and the oxygen supply system includes an oxygen supply pump and an oxygen manufacturing machine. The oxygen supply pump is connected with the output end of the oxygen manufacturing machine. An oxygen outlet disk is arranged at the output end of the oxygen supply pump. A plurality of oxygen outlet pipes are arranged on the oxygen outlet disk. A spiral extrusion column is arranged in the oxygen outlet disk. The spiral extrusion column is rotatably connected with the oxygen outlet disk. An extrusion shrapnel is arranged in the oxygen outlet pipe. An anaerobic box is arranged in the oxygen control pool. The anaerobic box is connected with the oxygen control pool. The anaerobic box is connected with the intermediate water pool. The anaerobic + anoxic + aerobic treatment process is adopted. The main function of anaerobic is to remove part of COD and release phosphorus contained in microorganisms. The main function of anoxic is to reduce the total nitrogen in sewage, and the anaerobic box is responsible for this operation. Aerobic treatment is mainly used to remove COD from sewage, oxidize some residual sulfides into sulfates, and better absorb phosphorus in sewage through microorganisms. At the same time, high-efficiency modified biological media are added. The biological media are spherical fillers. The oxygen outlet disc, under the action of the oxygen supply pump, sends the oxygen in the oxygen generator into the oxygen control pool. According to the different oxygen supply amounts, the conversion between aerobic and anoxic conditions is achieved. After the oxygen enters the oxygen outlet disc, the spiral extrusion column will rotate, thereby squeezing the oxygen into the oxygen outlet pipe. Under the action of the extrusion shrapnel, it enters the oxygen control pool at high speed, making the oxygen more dispersed, so that the oxygen can diffuse to multiple locations to ensure the best reaction state of the microorganisms.
[0011] A return water tray is provided in the oxygen outlet tray, an air return cylinder is provided in the return water tray, a multi-layer air permeable net is provided in the air return cylinder, a countercurrent device is provided on the oxygen supply pump, the countercurrent device is electrically connected to the oxygen supply pump through a wire, a return water port is provided on the oxygen outlet tray, and microorganism injectors are provided in the anaerobic box and the oxygen control pool respectively. When anoxic operation is performed, the countercurrent device is started, the oxygen supply pump will reverse, thereby generating negative pressure, sucking the tail water into the air return cylinder, and the internal air permeable net will fully separate the internal oxygen, and the oxygen will return to the oxygen generator under the action of negative pressure.
[0012] The disinfection component includes a disinfection track, on which a disinfection motor is arranged, a moving gear is arranged on the output end of the disinfection motor, the moving gear is meshed with teeth on the disinfection track, a disinfection rack is arranged on the disinfection motor, and an ultraviolet disinfector is arranged on the disinfection rack. The disinfection motor drives the moving gear to rotate, and the moving gear moves within the limitation of the disinfection track, and drives the disinfection rack to move, and at the same time drives the ultraviolet disinfector to move. The ultraviolet disinfector will disinfect the hot spring tail water and reduce the number of microorganisms.
[0013] The disinfection rack is provided with a surging rack, the surging rack is slidably connected with a lifting platform, a disinfection spring is provided between the lifting platform and the surging rack, a surging roller is provided on the lifting platform, a plurality of water storage tanks are provided on the surging roller, and a plurality of flow-following fan blades are provided on the surging roller. During the movement of the disinfection rack, the surging roller will also move in the middle water pool and rotate under the action of the flow-following fan blades. The water storage tanks on the surging roller will bring out part of the water, so that the water in the middle water pool can be fully surging and sterilized at multiple positions, thereby reducing the problem of omissions.
[0014] A hot spring tail water treatment process, the treatment process comprising:
[0015] S1. Hot spring wastewater is pumped into the regulating unit through the underground pumping station;
[0016] S2. The hot spring wastewater is coagulated and precipitated, and desulfurization agents and flocculants are added to remove suspended solids, sulfides and inorganic phosphorus in the wastewater. The added agents are polyferric and anionic polyacrylamide;
[0017] S3. Filter out impurities in wastewater and prepare oxygen regulation;
[0018] S4. Anaerobic residence time is 90-120min, anoxic residence time is 90-120min, aerobic residence time is 150-180min;
[0019] S5. The aerobic process is followed by an MBR reactor. Considering the water volume and land occupation, a curtain membrane is selected. Since the overall water quality of the hot spring tail water is relatively good, the flux is selected as 20L / (m2·d);
[0020] S6. Disinfect the wastewater after nanofiltration, and the final effluent meets the surface level Class III water effluent standard;
[0021] S7. After being treated, hot spring tail water can be discharged directly.
[0022] Compared with the prior art, the present invention has the following beneficial effects:
[0023] 1. The present invention adopts structural components with natural precipitation and extrusion molding to perform multi-level processing on hot spring tail water to prevent blockage problems and also reduce the problem that flocculated impurities cannot be separated from hot spring tail water in time.
[0024] 2. The present invention adopts an automatic oxygen control structural component, which can perform different degrees of treatment according to different conditions, can fully save space, and extract oxygen from the hot spring tail water to prevent the problem of microorganisms unable to dissipate in time due to internal oxygen residue. At the same time, the pressurized injection method can also increase the contact degree between oxygen and hot spring tail water.
[0025] 3. The present invention also takes into account that the water quality after normal MBR treatment can reach the surface quasi-Class III standard. Taking into account special circumstances such as water deterioration and extremely cold weather, a nanofiltration device is connected to the rear end of the MBR to ensure that the effluent is always qualified. At the same time, the disinfection component adopts an automatic surging structural component to ensure that the hot spring tail water is fully disinfected to avoid omissions. BRIEF DESCRIPTION OF THE DRAWINGS
[0026] Figure 1 It is a schematic diagram of the three-dimensional structure of the present invention;
[0027] Figure 2 It is a schematic diagram of the internal structure of the regulating unit of the present invention;
[0028] Figure 3 for Figure 2 The schematic diagram of the regulation structure of the local enlargement A in the middle;
[0029] Figure 4 It is a schematic diagram of the internal structure of the oxygen control pool of the present invention;
[0030] Figure 5 It is a schematic diagram of the internal structure of the oxygen outlet disk of the present invention;
[0031] Figure 6 It is a schematic diagram of the internal structure of the intermediate water tank of the present invention;
[0032] Figure 7 It is a schematic diagram of the internal structure of the reaction tank of the present invention;
[0033] Figure 8 It is a schematic diagram of the internal structure of the processing chamber of the present invention;
[0034] Fig. 9 It is a schematic diagram of the process structure of the present invention;
[0035] In the figure: 1, regulating unit; 2, submersible flow propeller; 3, water inlet pump; 4, sedimentation unit; 401, stirring zone; 402, sedimentation zone; 5, stirring assembly; 501, stirring motor; 502, stirring frame; 503, stirring blade; 504, drain outlet; 505, dosing pipe; 506, dosing device; 6, guide tube; 7, sedimentation assembly; 701, polymerization tank; 702, outlet tank; 703, squeezing box; 704, squeezing roller; 705, squeezing motor; 706, return water baffle; 8, transfer pump; 9, transfer pipe; 10, oxygen control tank; 11, filter tube; 12, reaction tank; 13, MBR reactor; 14, control valve; 16, intermediate water tank; 17, nanofiltration assembly; 18, disinfection assembly; 1801, disinfection track; 1802, disinfection electric machine; 1803, mobile gear; 1804, disinfection rack; 1805, ultraviolet disinfector; 1806, tumbling rack; 1807, lifting platform; 1808, disinfection spring; 1809, tumbling roller; 1810, flow fan blade; 19, discharge pipe; 20, mud discharge assembly; 2001, mud discharge motor; 2002, mud discharge wheel; 2003, mud discharge auxiliary wheel; 2004, mud discharge belt; 21, oxygen supply system; 2101, oxygen supply pump; 2102, oxygen generator; 2103, oxygen outlet disk; 2104, oxygen outlet pipe; 2105, spiral extrusion column; 2106, extrusion shrapnel; 2107, anaerobic box; 2108, return water disk; 2109, return air cylinder; 2110, breathable net; 2111, countercurrent device; 22, microbial injector; 23, treatment chamber. DETAILED DESCRIPTION
[0036] 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.
[0037] Example: Figure 1-Figure 9As shown, the present invention provides a technical solution, the treatment device includes a comprehensive treatment pool, the comprehensive treatment pool includes a regulating unit 1 and a sedimentation unit 4, the regulating unit 1 is equipped with a submersible flow propeller 2 and two water inlet pumps 3, the regulating unit 1 is connected with the sedimentation unit 4, the water inlet pump 3 is connected with the sedimentation unit 4, a stirring component 5 is arranged in the sedimentation unit 4, a guide tube 6 is arranged in the sedimentation unit 4, a sedimentation component 7 is arranged at the bottom of the sedimentation unit 4, a transfer pump 8 is arranged in the regulating unit 1, a transfer pipe 9 is arranged at the output end of the transfer pump 8, the end of the transfer pipe 9 away from the transfer pump 8 is connected with the oxygen control pool 10, the oxygen control pool 10 A filter tube 11 is arranged on the top, and the end of the filter tube 11 away from the oxygen regulating unit 10 is connected to the reaction tank 12, and an MBR reactor 13 is arranged in the reaction tank 12, and a control valve 14 is arranged on the reaction tank 12, and an intermediate water tank 16 is arranged at the end of the control valve 14 away from the reaction tank 12, and a treatment chamber 23 is arranged on the intermediate water tank 16, and a nanofiltration component 17 is arranged in the treatment chamber 23, and a disinfection component 18 is arranged in the intermediate water tank 16, and a discharge pipe 19 is arranged on the intermediate water tank 16, and the end of the discharge pipe 19 away from the intermediate water tank 16 is connected to the discharge tank. When disinfecting and removing impurities, the hot spring tail water is first sent to the regulating unit In the unit 1, the water inlet pump 3 on the submersible flow propeller 2 will extract the hot spring tail water, and then the hot spring tail water will be sent to the sedimentation unit 4, and then the stirring component 5 will work, and at the same time, flocculants and the like will be added to the regulating unit 1. Then, under the action of the flocculant, the sediment will fall into the sedimentation unit 4 and enter the guide tube 6. After being squeezed and formed by the guide tube 6, the flocculants can be fully deposited, so that the flocculants can play a full role. Then, the flocculants enter the mud discharge component 7 with the water for pressurization. Finally, the mud discharge component 7 will discharge the flocculants from the sedimentation unit, and also reduce the mixing of some smaller flocculants. Into the subsequent treatment operation, improve the accuracy of purification, the filtered water will be sent to the vicinity of the guide tube 6, and then the hot spring tail water will enter the oxygen control tank 10, the oxygen control tank 10 cooperates to control the oxygen content, and then the treated hot spring tail water will be sent to the reaction tank, the MBR reactor 13 can ensure the clarity of the effluent, and can choose a suitable flat membrane or curtain membrane based on comprehensive considerations such as the amount of water treated, investment budget and floor space, and then the reacted hot spring tail water will be sent to the intermediate water tank 16, and the tail water will finally be disinfected by the disinfection component 18 and finally meet the discharge standards.
[0038] The sedimentation unit 4 includes a stirring zone 401 and a sedimentation zone 402. The stirring component 5 is arranged in the stirring zone 401. The stirring component 5 includes a stirring motor 501 and a stirring frame 502. A plurality of stirring blades 503 are arranged on the stirring frame 502. The stirring frame 502 is arranged on the output end of the stirring motor 501. A drain port 504 is arranged on the sedimentation zone 402. The drain pipe 504 is connected with the regulating unit 1. A dosing pipe 505 is arranged in the regulating unit 1. A dosing pipe 505 is arranged in the dosing pipe 505. A doser 506 is arranged in the dosing pipe 505. After the hot spring tail water enters the stirring zone 401, a flocculant is added thereto. Then the stirring motor 501 will drive the stirring frame 502 to rotate. The stirring blades 503 will accelerate the combination of the flocculant and the hot spring tail water. Then the flocculated impurities will enter the sedimentation zone 402, waiting for the sedimentation component 7 to discharge these impurities out of the equipment. Finally, the hot spring tail water that has been discharged is sent to the drain pipe 504 and enters the regulating unit 1.
[0039] A sedimentation component 7 is arranged in the sedimentation area 402, and the sedimentation component 7 includes a polymerization tank 701. A mud discharge component 20 is arranged in the polymerization tank 701. The mud discharge component 20 includes a mud discharge motor 2001 and a mud discharge wheel 2002. The mud discharge wheel 2002 is arranged on the output end of the mud discharge motor 2001, and the mud discharge motor 2001 is arranged in the polymerization tank 701. A mud discharge auxiliary wheel 2003 is arranged in the polymerization tank 701. A mud discharge belt 2004 is wound around the mud discharge wheel 2002 and the mud discharge auxiliary wheel 2003. When the flocculated impurities enter the polymerization tank 701, the mud discharge motor 2001 will drive the mud discharge wheel 2002 to rotate, and the mud discharge wheel 2002 will drive the mud discharge belt to rotate. The flocculated impurities that have settled will be accumulated in the sedimentation area 402, waiting to be drained and removed. At the same time, the flocculated impurities are prevented from clogging the drainage pipe 504 and causing the problem of water being unable to discharge.
[0040] A water outlet trough 702 and a squeezing box 703 are provided in the polymerization tank 701. The water outlet trough 702 is connected to the drain pipe 504. An extrusion roller 704 and an extrusion motor 705 are provided in the squeezing box 703. The extrusion roller 704 is arranged on the output end of the extrusion motor 705. A backwater baffle plate 706 is provided on the squeezing box 703. A plurality of water flow troughs are opened on the squeezing roller 704. The backwater baffle plate 706 and the squeezing roller 704 are in intermittent sliding contact. After the flocculants enter the squeezing box 703, the squeezing motor 705 drives the squeezing roller 704 to rotate, thereby squeezing the impurities and tail water together into the vicinity of the backwater baffle plate 706. The backwater baffle plate 706 cooperates with the squeezing roller 704 to squeeze and separate the tail water rich in impurities. The squeezed water will flow out from the water flow trough, and the impurities will be sent back to the polymerization tank 701.
[0041] An oxygen supply system 21 is provided in the oxygen regulating unit 1, and the oxygen supply system 21 includes an oxygen supply pump 2101 and an oxygen generator 2102. The oxygen supply pump 2101 is connected to the output end of the oxygen generator 2102. An oxygen outlet disk 2103 is provided at the output end of the oxygen supply pump 2101. A plurality of oxygen outlet pipes 2104 are provided on the oxygen outlet disk 2103. A spiral extrusion column 2105 is provided in the oxygen outlet disk 2103. The spiral extrusion column 2105 is rotatably connected to the oxygen outlet disk 2103. An extrusion shrapnel 2106 is provided in the oxygen outlet pipe 2104. An anaerobic box 2107 is provided in the oxygen control pool 10. The anaerobic box 2107 is connected to the oxygen control pool 10. The anaerobic box 2107 is connected to the intermediate water pool 16. An anaerobic + anoxic + aerobic treatment process is adopted. The main function of anaerobic treatment is to remove part of COD and release phosphorus contained in microorganisms, and the main function of anoxic treatment is to remove part of COD and release phosphorus contained in microorganisms. In order to reduce the total nitrogen in the sewage, the anaerobic box 2107 is responsible for this operation. The aerobic box 2107 is mainly used to remove COD in the sewage, oxidize some residual sulfides into sulfates, and better absorb phosphorus in the sewage through microorganisms. At the same time, high-efficiency modified biological media are added. The biological media are spherical fillers. The oxygen outlet disk 2103, under the action of the oxygen supply pump 2101, sends the oxygen in the oxygen generator 2102 into the oxygen control pool 10. According to the different oxygen supply amounts, the conversion between aerobic and anoxic is realized. After the oxygen enters the oxygen outlet disk 2103, the spiral extrusion column 2105 will rotate, thereby squeezing the oxygen into the oxygen outlet pipe 2104. Under the action of the extrusion shrapnel 2106, it enters the oxygen control pool 10 at high speed, making the oxygen more dispersed, so that the oxygen can diffuse to multiple positions to ensure the optimal reaction state of the microorganisms.
[0042] A return water tray 2108 is provided in the oxygen outlet tray 2103, and a return air cylinder 2109 is provided in the return water tray 2108. A multi-layer air permeable net 2110 is provided in the return air cylinder 2109. A countercurrent device 2111 is provided on the oxygen supply pump 2101, and the countercurrent device 2111 is electrically connected to the oxygen supply pump 2101 through a wire. A return water port is provided on the oxygen outlet tray 2103, and microorganism injectors are respectively provided in the anaerobic box 2107 and the oxygen control pool 10. When anoxic operation is performed, the countercurrent device 2111 is started, the oxygen supply pump 2101 will reverse, thereby generating negative pressure, sucking the tail water into the return air cylinder 2109, and the internal air permeable net 2110 will fully separate the internal oxygen, and the oxygen will return to the oxygen generator under the action of negative pressure.
[0043] The disinfection component 18 includes a disinfection track 1801, on which a disinfection motor 1802 is provided, and a moving gear 1803 is provided on the output end of the disinfection motor 1802, and the moving gear 1803 is meshed with the teeth on the disinfection track 1801, and a disinfection rack 1804 is provided on the disinfection motor 1802, and an ultraviolet disinfector 1805 is provided on the disinfection rack 1804. The disinfection motor 1802 drives the moving gear 1803 to rotate, and the moving gear 1803 moves under the restriction of the disinfection track 1801, and drives the disinfection rack 1804 to move, and at the same time drives the ultraviolet disinfector 1805 to move, and the ultraviolet disinfector 1805 will disinfect the hot spring tail water to reduce the number of microorganisms.
[0044] The disinfection rack 1804 is provided with a surging rack 1806, and a lifting platform 1807 is slidably connected to the surging rack 1806. A disinfection spring 1808 is provided between the lifting platform 1807 and the surging rack 1806. The lifting platform 1807 is provided with a surging roller 1809, and a plurality of water storage tanks are provided on the surging roller 1809. A plurality of follow-flow fan blades 1810 are provided on the surging roller 1809. During the movement of the disinfection rack 1804, the surging roller 1809 will also move in the middle water pool 16 and rotate under the action of the follow-flow fan blades 1810. The water storage tanks on the surging roller 1809 will bring out part of the water therein, so that the water in the middle water pool 16 can be fully surging and sterilized at multiple positions, thereby reducing the problem of omissions.
[0045] A hot spring tail water treatment process, the treatment process comprising:
[0046] S1. Hot spring wastewater is pumped into the regulating unit 1 through the underground pump station;
[0047] S2. The hot spring wastewater is coagulated and precipitated, and a desulfurization agent and a flocculant are added to remove suspended solids, sulfides and inorganic phosphorus in the wastewater. The added agents are polyferric and anionic polyacrylamide;
[0048] S3. Filter out impurities in wastewater and prepare for oxygen regulation;
[0049] S4. Anaerobic residence time is 90-120min, anoxic residence time is 90-120min, aerobic residence time is 150-180min;
[0050] S5. The aerobic process is followed by an MBR reactor 13. Considering the water volume and land occupation, a curtain membrane is selected. Since the overall water quality of the hot spring tail water is relatively good, the flux is selected to be 20L / (m2·d);
[0051] S6. Disinfect the wastewater after nanofiltration, and the final effluent meets the surface level Class III water effluent standard;
[0052] S7. After being treated, hot spring tail water can be discharged directly.
[0053] Working principle: When disinfecting and removing impurities, first send the hot spring tail water into the regulating unit 1, the water inlet pump 3 on the submersible flow propeller 2 will extract the hot spring tail water, and then the hot spring tail water will be sent to the sedimentation unit 4, and then the stirring component 5 will work. After the hot spring tail water enters the stirring area 401, flocculant is added to it, and then the stirring motor 501 will drive the stirring frame 502 to rotate, and at the same time, flocculant is added to the regulating unit 1. Then, under the action of the flocculant, the sediment will fall into the sedimentation unit 4 and enter the diversion unit 4. In the cylinder, the guide cylinder pressurizes the flocculants, and then the internal sedimentation component 7 is started to work. The extrusion motor 705 drives the extrusion roller 704 to rotate, so as to squeeze the impurities and tail water together into the vicinity of the return water baffle 706. The return water baffle 706 cooperates with the extrusion roller 704 to squeeze and separate the tail water rich in impurities, and the water therein will be discharged. The filtered water will be sent to the vicinity of the guide cylinder 6, and then these hot spring tail water will enter the oxygen control pool 10, and the oxygen control pool 10 cooperates with the control oxygen The oxygen content is determined by the oxygen supply pump 2101, and the oxygen-free box 2107 is responsible for the oxygen-free consumption operation. Then, the treated hot spring tail water will be sent to the reaction tank. The oxygen outlet plate 2103, under the action of the oxygen supply pump 2101, sends the oxygen in the oxygen generator 2102 to the oxygen control tank 10. According to the different oxygen supply amounts, the conversion between aerobic and anoxic is realized. After the oxygen enters the oxygen outlet plate 2103, the spiral extrusion column 2105 will rotate, thereby squeezing the oxygen into the oxygen outlet pipe 2104. The MBR reactor 13 can ensure that the effluent is clear, and can be used according to the treated water. Taking into account the quantity, investment budget and floor space, a suitable flat membrane or curtain membrane is selected, and then the hot spring tail water after the reaction is sent to the intermediate water pool 16. The tail water is finally disinfected by the disinfection component 18, and the disinfection motor 1802 drives the moving gear 1803 to rotate. The moving gear 1803 moves under the restriction of the disinfection track 1801, and drives the disinfection rack 1804 to move, and at the same time drives the ultraviolet sterilizer 1805 to move. The ultraviolet sterilizer 1805 will disinfect the hot spring tail water and finally meet the discharge standards.
[0054] It will be apparent to those skilled in the art that the invention is not limited to the details of the exemplary embodiments described above and that the invention can be implemented in other specific forms without departing from the spirit or essential features of the invention. Therefore, the embodiments should be considered exemplary and non-limiting in all respects, and the scope of the invention is defined by the appended claims rather than the foregoing description, and it is intended that all variations falling within the meaning and scope of the equivalent elements of the claims be included in the invention. Any reference numeral in a claim should not be considered as limiting the claim to which it relates.
Claims
1. A hot spring tail water treatment device, characterized in that: The treatment device comprises a comprehensive treatment pool, wherein the comprehensive treatment pool comprises a regulating unit (1) and a sedimentation unit (4), wherein the regulating unit (1) is equipped with a submersible flow propeller (2) and two water inlet pumps (3), wherein the regulating unit (1) is in communication with the sedimentation unit (4), wherein the water inlet pump (3) is in communication with the sedimentation unit (4), wherein a stirring assembly (5) is arranged in the sedimentation unit (4), wherein a flow guide tube (6) is arranged in the sedimentation unit (4), wherein a sedimentation assembly (7) is arranged at the bottom of the sedimentation unit (4), wherein a transfer pump (8) is arranged in the regulating unit (1), wherein a transfer pipe (9) is arranged at the output end of the transfer pump (8), wherein the end of the transfer pipe (9) away from the transfer pump (8) is in communication with an oxygen control pool (10), wherein The oxygen control tank (10) is provided with a filter tube (11), one end of the filter tube (11) away from the oxygen adjustment unit (10) is connected to the reaction tank (12), an MBR reactor (13) is arranged in the reaction tank (12), a control valve (14) is arranged on the reaction tank (12), an intermediate water tank (16) is arranged at one end of the control valve (14) away from the reaction tank (12), a treatment chamber (23) is arranged on the intermediate water tank (16), a nanofiltration component (17) is arranged in the treatment chamber (23), a disinfection component (18) is arranged in the intermediate water tank (16), a discharge pipe (19) is arranged on the intermediate water tank (16), and one end of the discharge pipe (19) away from the intermediate water tank (16) is connected to the discharge tank.
2. A hot spring tail water treatment device according to claim 1, characterized in that: The sedimentation unit (4) comprises a stirring zone (401) and a sedimentation zone (402); the stirring assembly (5) is arranged in the stirring zone (401); the stirring assembly (5) comprises a stirring motor (501) and a stirring frame (502); the stirring frame (502) is provided with a plurality of stirring blades (503); the stirring frame (502) is arranged on the output end of the stirring motor (501); a drainage port (504) is provided on the sedimentation zone (402); the drainage pipe (504) is connected to the regulating unit (1); a dosing pipe (505) is provided in the regulating unit (1); a dosing device (506) is provided in the dosing pipe (505).
3. A hot spring tail water treatment device according to claim 2, characterized in that: A sedimentation component (7) is arranged in the sedimentation area (402), the sedimentation component (7) comprises a polymerization tank (701), a mud discharge component (20) is arranged in the polymerization tank (701), the mud discharge component (20) comprises a mud discharge motor (2001) and a mud discharge wheel (2002), the mud discharge wheel (2002) is arranged on the output end of the mud discharge motor (2001), the mud discharge motor (2001) is arranged in the polymerization tank (701), a mud discharge auxiliary wheel (2003) is arranged in the polymerization tank (701), and a mud discharge belt (2004) is wound around the mud discharge wheel (2002) and the mud discharge auxiliary wheel (2003).
4. A hot spring tail water treatment device according to claim 3, characterized in that: The aggregation tank (701) is provided with a water outlet trough (702) and a water squeezing box (703); the water outlet trough (702) is connected to a drainage pipe (504); the water squeezing box (703) is provided with an extrusion roller (704) and an extrusion motor (705); the extrusion roller (704) is arranged on the output end of the extrusion motor (705); the water squeezing box (703) is provided with a backwater baffle plate (706); a plurality of water flow grooves are provided on the extrusion roller (704); the backwater baffle plate (706) is in intermittent sliding contact with the extrusion roller (704).
5. A hot spring tail water treatment device according to claim 1, characterized in that: The oxygen regulating unit (10) is provided with an oxygen supply system (21), and the oxygen supply system (21) comprises an oxygen supply pump (2101) and an oxygen generator (2102). The oxygen supply pump (2101) is connected to the output end of the oxygen generator (2102). The output end of the oxygen supply pump (2101) is provided with an oxygen outlet disk (2103), and the oxygen outlet disk (2103) is provided with a plurality of oxygen outlet pipes (2104). A spiral extrusion column (2105) is arranged in the disk (2103), and the spiral extrusion column (2105) is rotatably connected to the oxygen outlet disk (2103). An extrusion spring (2106) is arranged in the oxygen outlet pipe (2104). An anaerobic box (2107) is arranged in the oxygen control pool (10), and the anaerobic box (2107) is connected to the oxygen control pool (10). The anaerobic box (2107) is connected to the intermediate water pool (16).
6. A hot spring tail water treatment device according to claim 5, characterized in that: The oxygen outlet disk (2103) is provided with a water return disk (2108), the water return disk (2108) is provided with a return air cylinder (2109), the return air cylinder (2109) is provided with a multi-layer air permeable net (2110), the oxygen supply pump (2101) is provided with a countercurrent device (2111), the countercurrent device (2111) is electrically connected to the oxygen supply pump (2101) through a wire, the oxygen outlet disk (2103) is provided with a water return port, and the anaerobic box (2107) and the oxygen control pool (10) are respectively provided with microorganism fillers (22).
7. A hot spring tail water treatment device according to claim 1, characterized in that: The disinfection assembly (18) comprises a disinfection track (1801), a disinfection motor (1802) is arranged on the disinfection track (1801), a moving gear (1803) is arranged on the output end of the disinfection motor (1802), the moving gear (1803) is meshed with teeth on the disinfection track (1801), a disinfection rack (1804) is arranged on the disinfection motor (1802), and an ultraviolet disinfector (1805) is arranged on the disinfection rack (1804).
8. A hot spring tail water treatment device according to claim 8, characterized in that: The disinfection rack (1804) is provided with a surging rack (1806), the surging rack (1806) is slidably connected with a lifting platform (1807), a disinfection spring (1808) is provided between the lifting platform (1807) and the surging rack (1806), the lifting platform (1807) is provided with a surging roller (1809), the surging roller (1809) is provided with a plurality of water storage tanks, and the surging roller (1809) is provided with a plurality of flow-following blades (1810).
9. A hot spring tail water treatment process, characterized in that: The treatment process includes: S1. Hot spring wastewater is pumped into containers through an underground pumping station; S2. Coagulate and precipitate the hot spring wastewater and add desulfurization agent; S3. Filter out impurities in wastewater and prepare for oxygen regulation; S4. Anaerobic residence time is 90-120min, anoxic residence time is 90-120min, aerobic residence time is 150-180min; S5. Perform nanofiltration treatment on the wastewater; S6. Disinfect the wastewater after nanofiltration, and the final effluent meets the surface level Class III water effluent standard; S7. After being treated, hot spring tail water can be discharged directly.
Citation Information
Patent Citations
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