CN107902808A - A kind of processing method and equipment for aquiculture sewerage discharge - Google Patents
A kind of processing method and equipment for aquiculture sewerage discharge Download PDFInfo
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- CN107902808A CN107902808A CN201711131204.9A CN201711131204A CN107902808A CN 107902808 A CN107902808 A CN 107902808A CN 201711131204 A CN201711131204 A CN 201711131204A CN 107902808 A CN107902808 A CN 107902808A
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- Prior art keywords
- water
- aquiculture sewerage
- aquiculture
- draining exit
- sewage draining
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Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/001—Processes for the treatment of water whereby the filtration technique is of importance
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/281—Treatment of water, waste water, or sewage by sorption using inorganic sorbents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/283—Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
- C02F1/46104—Devices therefor; Their operating or servicing
- C02F1/46109—Electrodes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
- C02F1/467—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
- C02F1/4672—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electrooxydation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F2001/007—Processes including a sedimentation step
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/16—Nitrogen compounds, e.g. ammonia
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/16—Nitrogen compounds, e.g. ammonia
- C02F2101/166—Nitrites
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/20—Heavy metals or heavy metal compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/005—Processes using a programmable logic controller [PLC]
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/04—Disinfection
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/14—Maintenance of water treatment installations
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/16—Regeneration of sorbents, filters
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F7/00—Aeration of stretches of water
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Water Treatment By Electricity Or Magnetism (AREA)
- Water Treatment By Sorption (AREA)
Abstract
The present invention announces a kind of processing method for aquiculture sewerage discharge, wherein, include the following steps：Step A, the aquiculture sewerage of aquaculture pond bottom discharge, by precipitating filter plant preliminary purification, removes the dirt not soluble in water such as suspended particulate and excrement；Step B, aquiculture sewerage passes through cleaning equipment, and the ammonia nitrogen that goes in water removal, nitrite, heavy metal, the harmful substance such as antibiotic are simultaneously sterilized；Step C, aquiculture sewerage passes through reduction apparatus, flocculent deposit, unnecessary cation and the Strong oxdiative thing for going impurity tiny in water removal, colloid protein to be formed；The aquiculture sewerage for completing purification reduction treatment is directly discharged into natural water body by discharge outlet.The present invention can reduce aquiculture sewerage fast purification, kill the germ in water body, virus, reduce ammonia nitrogen and content of nitrite, remove the harmful substance in water body, the water after processing can be directly discharged into natural water body.
Description
Technical field
The present invention relates to the process field of aquiculture sewerage discharge, various fresh water, brackish water and sea are especially adapted for use in
It is fresh temporarily that the aquaculture wastewater of aquatic organism, fresh water and sea-farming sewage, fresh water and seawater view and admire biological cultivation sewage, seafood and river
Support, the sewage discharge of the fresh transport of seafood and river processing.
Background technology
At present, breeding way is intensive culture pattern and industrial aquaculture pattern by pervious extensive cultivation, half intensive culture mode development,
But due to the economic benefit that covets, cultured area is continuously increased, cultivation density is continuously improved, and breed variety is excessively single, makes
The balance of natural ecosystems is broken in aquaculture system, and self-pollution is serious, produces substantial amounts of aquaculture wastewater.Aquatic products is supported
Broad-spectrum antibiotics are abused during growing to control the generation of disease, the resistance to the action of a drug of bacterium is added, more destroys aquaculture
The balance of waters normal bio fauna, so that forming vicious circle.Main pollutant has ammonia nitrogen, nitrous in aquiculture sewerage
Hydrochlorate, organic pollution, phosphorus and fouling organism.Aquiculture sewerage not by it is any processing be just directly discharged into river, river, lake,
The natural water bodies such as sea, make that eutrophication of natural water, antibiotic be exceeded, substrate ruins and induces a large amount of numerous of the pathogenic bacteria such as vibrios
Grow, cause disease frequent so that the ecosystem of natural water body is destroyed, and the ecosystem is unbalance, causes the disease-resistant of aquatic organism
Power reduces, and is more easy to infection pathogen.Currently, aquiculture sewerage processing is main uses：Physical technique, such as largely change water, aeration,
Filtering, precipitation, absorption, air supporting etc.；Chemical technology, such as flocculation, neutralization, complexing, redox, ozonization；Biotechnology,
Photosynthetic bacteria, Bacillus, actinomyces, more bacterium complex microorganism preparations, aquatic is added or cultivated such as in aquiculture sewerage
Plant, vegetables, flowers etc.；But these technologies are there are waste water resource, high energy consumption, system complex, it is cumbersome the problems such as, and
It is on the rise with the pollution of fishery water, substantial amounts of germ, virus, parasite, organic matter, antibiotic, a huge sum of money is incorporated in water
Belonging to and other harmful substances are very difficult to remove, aquiculture sewerage is arbitrarily discharged without processing, serious pollution natural water body,
So the problem of restoring nature after the bactericidal purifying of aquiculture sewerage is badly in need of solving.
The high speed development of culture fishery at present, the random discharge of breeding wastewater, natural water receive serious pollution,
So aquiculture sewerage discharge has to pass through processing.The processing method of traditional aquiculture sewerage discharge is mainly by heavy
Shallow lake pond removes the solid dirt do not allowed, and the harmful substances such as the ammonia nitrogen of water removal, nitrous acid are gone in biofilter, and ultraviolet and ozone carry out
Sterilization.There are the shortcomings of processing time is long, efficiency is low, high energy consumption, cumbersome, and regular maintenance is complicated.As aquaculture is dirty
The pollution getting worse of water, sewage quantity is more and more, and traditional aquiculture sewerage discharge treatment method cannot meet to work as
Preceding needs.It is badly in need of a kind of processing time is short, efficient, energy consumption is low, easy to operate, the simple aquiculture sewerage of regular maintenance
The processing method of discharge.
The content of the invention
In order to solve the treatment technology deficiency of existing aquiculture sewerage discharge, the present invention provides dirty for aquaculture
The processing method and equipment of water discharge, this method can not only kill germ, virus, parasite in water, reduce ammonia nitrogen and nitrous
Hydrochlorate concentration, goes soluble organic, antibiotic, the harmful substance such as heavy metal in water removal, also carries out reduction treatment to water body, make
The approximate free of contamination natural water body of water after processing；Equipment using modularized design is simple in structure, processing speed is fast, it is efficient,
Energy consumption is low, operation is easy, can also accurately be finely tuned according to various regions different quality and processing standard.
The present invention solves the technical solution that its technical problem uses：
To achieve these goals, the present invention provides a kind of processing method for aquiculture sewerage discharge, wherein,
Include the following steps：
Step A, the aquiculture sewerage of aquaculture pond bottom discharge, by precipitating filter plant preliminary purification, removes
The dirt not soluble in water such as suspended particulate and excrement；
Step B, aquiculture sewerage passes through cleaning equipment, removes ammonia nitrogen, nitrite, heavy metal, antibiotic in water removal
Etc. harmful substance and sterilize；
Step C, aquiculture sewerage passes through reduction apparatus, goes impurity tiny in water removal, colloid protein to be formed cotton-shaped
Precipitation, unnecessary cation and Strong oxdiative thing, the aquiculture sewerage for completing purification reduction treatment are directly discharged into by water outlet
The natural water bodies such as river, river, lake, sea.
Step A is specifically, aquiculture sewerage is carried from the bottom center sewage draining exit discharge of aquaculture pond by water pump
Rise, enter precipitation filter plant by water inlet c, primary purifying is carried out to aquiculture sewerage, water body first passes through water spray duckbilled
Precipitation tank is flowed into, removes remaining bait in water removal, bulky grain suspended matter, animal wastes, the thing not soluble in water such as algae of death
Matter, then aquiculture sewerage by precipitation process enter lautertuns by unrestrained water baffle, pass through filter media, removal
Tiny material not soluble in water in water, the aquiculture sewerage after filtering is entered by flow apron b and water level baffle b to catchment
Groove b, finally flows out from the water outlet c of catch basin b bottoms, completes preliminary purification processing, and the dirt isolated enters garbage pool, can
Recycled with working process as vegetable fertilizer；
Step B is carried out deeply net specifically, enter cleaning equipment by water inlet a by the aquiculture sewerage of step A
Change, cleaning equipment is made of cation generator and hydroxyl radical generator, and cation and hydroxyl can be produced by electrolysis
The Strong oxdiative thing such as free radical, cation and Strong oxdiative thing synergistic effect, can more quickly and efficiently kill bacterium in water, arc
Bacterium, virus, algae, parasite, reduce ammonia nitrogen and content of nitrite in aquiculture sewerage, remove in water body can be dissolved with
The harmful substances such as machine thing, antibiotic and heavy metal, aquiculture sewerage successively flow through cation generator and hydroxyl radical free radical hair
Purified treatment is goed deep into raw device, completion, and aquiculture sewerage is flowed out by water outlet a；
Step C by water inlet b by the aquiculture sewerage of step B specifically, enter reduction apparatus, by spray tube
Into reduction cell, Air Exposure carries out water body by nanometer aeration disk first in reduction cell, aeration can accelerate water body
Flocculation reaction, forms tiny suspended particulate and colloid protein that aquiculture sewerage produces in step B purification process cotton-shaped
Precipitation, then carries out reduction treatment by multilayer reducing medium to water body, removes aquiculture sewerage and is produced in aeration process
Flocculent deposit, while adsorb cation unnecessary in water, remove unnecessary Strong oxdiative material, revert to aquiculture sewerage
The state of approximate natural water, the aquiculture sewerage by reduction treatment flow into catch basin by flow apron a and water level baffle a
A, the aquiculture sewerage for finally completing purification reduction treatment are directly discharged into the natural waters such as river, river, lake, sea by water outlet b.
Further, the reduction inside the precipitation tank inside precipitation filter plant, lautertuns and catch basin b, reduction apparatus
Groove and catch basin a are respectively equipped with independent sewage draining exit, and sewage is directly entered garbage pool by independent blow-off line, avoids sewage
Reflux mutually pollution.
Further, the filter medium for precipitating the filling of filter plant self-filtering groove is fine sand, coarse sand, and ratio is：5:2,
Divide two layers of filling from top to bottom in the order described above.
Further, the reducing medium of reduction apparatus filling is quartz sand, medical stone, porous carbon, active zeolite, and ratio is
3:2:6:4, divide four layers of filling from top to bottom in the order described above.
In order to preferably realize the object of the invention, the present invention discloses a kind of processing for aquiculture sewerage discharge again
The device therefor of method, including：Precipitate filter plant, cleaning equipment, reduction apparatus.
Wherein, the precipitation filter plant of step A is babinet c structures, and the babinet c is by precipitation tank, lautertuns, catch basin b
Composition；The side of the babinet c is equipped with a water inlet c, water inlet of removing contamination, backwash water inlet and discharge outlet of removing contamination, opposite side
Equipped with before water outlet a c, the babinet c be equipped with sewage draining exit d, sewage draining exit e, sewage draining exit f；The babinet c is internally provided with unrestrained
Water baffle, flow apron b and water level baffle b, the unrestrained water baffle is between precipitation tank and lautertuns, the flow apron b
And water level baffle b is between lautertuns and catch basin b；The precipitation trench bottom be form of pot bottom, in the circumferential direction bottom of bottom four
The heart tilts, and bottom centre is equipped with center sewage draining exit, and the bottom is surrounded by nozzle of removing contamination；The precipitation tank top is equipped with water spray
Duckbilled, the water spray duckbilled are connected with water inlet c；The lautertuns lower part was equipped with water-bed plate, was filled on the excessively water-bed plate
Filter medium；Cross between water-bed plate and filter medium and bury backwash water pipe.The sewage draining exit d is located at lautertuns front upper, institute
State sewage draining exit f and be located at lautertuns front bottom；The water outlet c is located at mono- side bottoms of catch basin b, and the sewage draining exit e is positioned at collection
Sink b front bottoms.
Further, the filter medium of filling is coarse sand and fine sand in the lautertuns.
Further, the backwash tube in the lautertuns carries out automatic backwash to automatically control to filter medium.
Further, the nozzle of removing contamination of the precipitation trench bottom is to automatically control, and auto-flushing is carried out to the dirt of bottom.
The cleaning equipment of step B is babinet a structures, by cation generator, hydroxyl radical generator, valve a, valve
B, valve c and control module composition, the babinet a both sides are equipped with water inlet a and water outlet a；The cation generator and institute
State hydroxyl radical generator to connect by PVC pipeline, valve c is set on the pipeline；The hydroxyl radical generator with
Water inlet a is connected by PVC pipeline, and valve a is set on the pipeline；The cation generator passes through pvc pipe with water outlet a
Road connects, and valve b is set on the pipeline；Fixed screw is equipped with the inside of the babinet a, control module is fixed on the inner wall of babinet
On, the control module is made of shell, working power, stand-by power supply and the PLC of setting inside the shell；The cation occurs
The shell of device is bonded by PVC groove a and PVC flanges a and formed, and cation generator enclosure installs integrated Kufil electricity
Pole group；The copper silver ion alloy electrode group is made of even number Kufil gold plaque, the spacing ＜ 10mm of two neighboring electrode slice；
The shell of the hydroxyl radical generator is bonded by PVC groove b and PVC flanges b and formed, hydroxyl radical generator enclosure
Integrated coated titanium electrode group is installed；The coated titanium electrode group is made of odd number coated titanium electrode piece, two neighboring electricity
The spacing ＜ 10mm of pole piece.
As a preferred embodiment of the present invention, the cation generator both ends are respectively provided with a PVC ring flange, institute
State PVC ring flanges and be equipped with binding post；The hydroxyl radical generator both ends are respectively provided with a titanium ring flange, the titanium flange
Disk is equipped with binding post.
Further, the Kufil gold plaque is divided into two groups, is separately fixed on PVC ring flanges and PVC disks；The coating
Ti electrode piece is divided into fixed electrode film and extends two kinds of electrode slice, and the fixed electrode film is divided into two groups, is separately fixed at titanium dish
On titanium ring flange, the fixed electrode film is odd-level, and one layer of extension electrode slice is equipped between adjacent two panels fixed electrode film,
The extension electrode slice is fixed on the gap location between adjacent two panels fixed electrode film, the extension electrode by polyamide bolt
Piece is even level.
Further, the Kufil gold plaque is connected by copper conductor with the binding post on PVC flanges.
Further, the shell both sides of the control module are equipped with thermovent, and control module front end face is equipped with manual adjustment
Knob, power supply indicator, work light and USB port.
Preferably, binding post and electricity are passed through between the control module and cation generator and hydroxyl radical generator
Cable is connected.
Preferably, connected between PVC ring flanges and PVC the flanges a by stainless steel bolt；The titanium ring flange and
It is bolted between PVC flanges b by titanium.
As a preferred embodiment of the present invention, two flowing water mouths are offered on the shell of the cation generator.
Two flowing water mouths are offered on the shell of the hydroxyl radical generator.
The reduction apparatus of step C is babinet b structures, and side is equipped with air inlet and recoil water inlet, and opposite side is equipped with water outlet
Mouth b, top, which is equipped with before water inlet b, the babinet b, is equipped with sewage draining exit a, sewage draining exit b, sewage draining exit c；It is equipped with the babinet b
Flow apron a and water level baffle a, by babinet, b points are reduction cell and catch basin a；The sewage draining exit a is arranged on bottom before reduction cell
Portion, the sewage draining exit b are arranged on reduction cell front upper；Water tray, recoil water pipe, reduction Jie were equipped with the reduction cell
Matter, nanometer aeration disk and spray tube, the spray tube is located at the top of reduction cell to be connected with water inlet b；The reducing medium filling
Above water tray, the nanometer aeration disk is located above reducing medium excessively, the water outlet b is located at the side of catch basin a, institute
State the front bottom that sewage draining exit c is located at catch basin a.
Further, the reducing medium in the reduction cell is quartz sand, medical stone, porous carbon and active zeolite powder.
Further, the recoil water pipe is arranged on bottom quartz sand, medical stone top.
Further, the backwash tube in the reduction cell carries out automatic backwash to automatically control to quartz sand.
Compared with prior art, the present invention has the advantages that：
The aquiculture sewerage of aquaculture pond discharge is rapidly carried out purification reduction by the present invention, not only can effectively be killed
Germ, virus in water body, reduce ammonia nitrogen and content of nitrite in water used for aquiculture, can also remove in water body can
The harmful substances such as molten organic matter, antibiotic and heavy metal, make breeding water quickly revert to approximate free of contamination natural water body.
The present invention can not only be by aquiculture sewerage body fast purification, and reverts to approximate free of contamination natural water shape
State, also have the advantages that water-saving, efficient, energy consumption is low, simple in structure, the Automation Design, simple operation, it is good in parameter setting
Afterwards, without that need not be adjusted in special circumstances, the labor intensity of worker can be greatly lowered.
The principle of electrolysis water is applied to circulating water cultivation field by the present invention, existing aquiculture sewerage can be replaced to discharge
Protein Skimmer, biofilter, ultraviolet sterilization and ozone sterilization device in processing method.Using cation generator and
The combination of two kinds of Different electrodes of hydroxyl radical generator, two kinds of electrode synergistic effects, makes water treatment efficiency than individually make
Three times are improved with a kind of electrode；Designed at the same time using advanced electrode group structure, work efficiency is high, less scaling；The present invention's
Equipment power dissipation is extremely low, stable equipment operation, processing water it is efficient；Only 0.003 degree of consumption is electric for one ton of processing water one hour；This hair
It is bright to be cleaned using automatic, without manual maintenance, treatment effect will not be reduced in the case of working long hours；The present invention passes through water quality
Probe monitors water quality is monitored, is run by PLC automatic control equipments, is greatly reduced the workload of operating personnel, mitigates behaviour
Make the burden of personnel.
Brief description of the drawings
The present invention is further described with reference to the accompanying drawings and examples.
Fig. 1 is the equipment assembling schematic diagram of the present invention.
Fig. 2 is the internal structural map of Fig. 1 cleaning equipments of the present invention.
Fig. 3 is the internal structural map of Fig. 1 reduction apparatus of the present invention.
Fig. 4 is the internal structural map of Fig. 1 precipitations filter plant of the present invention.
Fig. 5 is the internal structural map of Fig. 2 cation generators of the present invention.
Fig. 6 is the external structure figure of Fig. 2 cation generators of the present invention.
Fig. 7 is the internal structural map of Fig. 2 hydroxyl radical generators of the present invention.
Fig. 8 is the external structure figure of Fig. 2 hydroxyl radical generators of the present invention.
Fig. 9 is the external structure figure of Fig. 2 control modules of the present invention.
Figure 10 is the control principle drawing of the present invention.
Figure 11 is the ammonia nitrogen change comparison diagram of aquiculture sewerage.
Figure 12 is the nitrite change comparison diagram of aquiculture sewerage.
Figure 13 is the bacterium change comparison diagram of aquiculture sewerage.
Figure 14 is the vibrios change comparison diagram of aquiculture sewerage.
In figure：1. aquaculture pond, 2. central blow-down mouths, 3. water pumps, 4. precipitation filter plants, 5. cleaning equipments, 6. also
Original equipment, 7. pressure pumps, 8. air blowers, 9. water inlet a, 10. cation generators, 11. valve a, 12. control modules, 13.
Hydroxyl radical generator, 14. water outlet a, 15. valve b, 16. valve c, 17. babinet a, 18. sewage draining exit a, 19. porous carbons,
20. medical stone, 21. recoil water pipes, 22. quartz sands, 23. recoil water inlets, 24. air inlets, 25. reduction cells, 26. water inlet b,
27. spray tube, 28. nanometer aeration disks, 29 sewage draining exit b, 30. catch basin a, 31. babinet b, 32. water level baffle a, 33. water outlets
B, 34. sewage draining exit c, 35. flow apron a, 36. active zeolite powder, 37. cross water trays, and 38. remove contamination discharge outlet, 39. backwashes water inlet
Mouthful, 40. remove contamination water inlet, and 41. remove contamination nozzle, 42. water inlet c, 43. water spray duckbilleds, 44. purification tanks, 45. unrestrained water baffles, and 46.
Sewage draining exit d, 47 lautertuns, 48. fine sands, 49. catch basin b, 50, babinet c, 51. water outlet c, 52. sewage draining exit e, 53. water levels gear
Plate b, 54. flow apron b, 55. excessively water-bed plates, 56. coarse sands, 57. backwash water pipes, 58. sewage draining exit f, 59. center sewage draining exits, 60.
Stainless steel binding post, 61.PVC ring flanges, 62. Kufil electrode groups, 63. Kufil gold plaques, 64.PVC disks, 65.PVC flanges
A, 66. flowing water mouth a, 67.PVC groove a, 68. stainless steel bolts, 69. titanium binding posts, 70. titanium ring flanges, 71. coated titanium electrode pieces,
72. coated titanium electrode group, 73. polyamide bolts, 74. titanium dish, 75.PVC flanges b, 76. flowing water mouth b, 77. titanium bolts, 78.PVC
Groove b, 79. power supply indicators, 80. shells, 81. thermovents, 82. manual adjustment knobs, 83.USB mouthfuls, 84. work lights.
Embodiment
To make the purpose, technical scheme and advantage of the embodiment of the present invention clearer, below in conjunction with the embodiment of the present invention
In attached drawing, the technical solution in the embodiment of the present invention is clearly and completely described, it is clear that described embodiment is
The part of the embodiment of the present invention, instead of all the embodiments.Based on the embodiments of the present invention, ordinary skill people
Member's all other embodiments obtained without creative efforts, belong to protection scope of the present invention.
As shown in Fig. 1 to Fig. 9, Fig. 1 is the equipment assembling schematic diagram of the present invention.Fig. 2 is Fig. 1 cleaning equipments of the present invention
Internal structural map.Fig. 3 is the internal structural map of Fig. 1 reduction apparatus of the present invention.Fig. 4 is the interior of Fig. 1 precipitations filter plant of the present invention
Cage structure figure.Fig. 5 is the internal structural map of Fig. 2 cation generators of the present invention.Fig. 6 is Fig. 2 cation generators of the present invention
External structure figure.Fig. 7 is the internal structural map of Fig. 2 hydroxyl radical generators of the present invention.Fig. 8 is Fig. 2 hydroxyl frees of the present invention
The external structure figure of base generator.Fig. 9 is the external structure figure of Fig. 2 control modules of the present invention.
A kind of method for treating water for circulating water cultivation of the invention, wherein, include the following steps：
Step A, the aquiculture sewerage of 1 bottom of aquaculture pond discharge, by precipitating 4 preliminary purification of filter plant, goes
Except the dirt not soluble in water such as suspended particulate and excrement；
Step B, aquiculture sewerage passes through cleaning equipment 5, removes ammonia nitrogen, nitrite, heavy metal, antibiotic in water removal
Etc. harmful substance and sterilize；
Step C, aquiculture sewerage passes through reduction apparatus 6, goes impurity tiny in water removal, colloid protein to be formed cotton-shaped
Precipitation, unnecessary cation and Strong oxdiative thing, the aquiculture sewerage for completing purification reduction treatment are directly discharged into by water outlet
The natural water bodies such as river, river, lake, sea.
Step A is specifically, aquiculture sewerage is discharged from the bottom center sewage draining exit 2 of aquaculture pond 1, by water pump 3
Lifting enters precipitation filter plant 4 by water inlet c42, carries out primary purifying to aquiculture sewerage, water body first passes through water spray
Duckbilled 43 enters precipitation tank 44, goes remaining bait in water removal, bulky grain suspended matter, animal wastes, the algae etc. of death insoluble
In the material of water, then the aquiculture sewerage by precipitation process, which passes through, overflows water baffle 45 into lautertuns 47, passes through filtering
Medium, removes tiny material not soluble in water in water removal, complete the aquiculture sewerage of filtration treatment by flow apron b54 and
Water level baffle b53 enters catch basin b49, is finally flowed out from the water outlet c51 of catch basin b49 bottoms, completes preliminary purification processing,
The dirt isolated enters garbage pool, can be recycled with working process as vegetable fertilizer；
Step B is goed deep into specifically, enter cleaning equipment 5 by water inlet a9 by the aquiculture sewerage of step A
Purification, cleaning equipment 5 are made of cation generator 10 and hydroxyl radical generator 13, and cation can be produced by electrolysis
Act synergistically, can more quickly and efficiently kill thin in water with Strong oxdiative thing, cation and Strong oxdiative things such as hydroxyl radical free radicals
Ammonia nitrogen and content of nitrite in bacterium, vibrios, virus, algae, parasite, reduction aquiculture sewerage, remove in water body
The harmful substances such as soluble organic, antibiotic and heavy metal, aquiculture sewerage successively flow through cation generator 10 and hydroxyl
Purified treatment is goed deep into free-radical generator 13, completion, and aquiculture sewerage is flowed out by water outlet a14；
Step C by water inlet b26 by the aquiculture sewerage of step B specifically, enter reduction apparatus, by spray
Pipe 27 enters reduction cell 25, and Air Exposure is carried out to water body by nanometer aeration disk 28 first in the reduction cell 25, and aeration can be with
Accelerate the flocculation reaction of water body, tiny suspended particulate and the colloid egg for making aquiculture sewerage be produced in step B purification process
It is white to form flocculent deposit, reduction treatment is then carried out to water body by multilayer reducing medium, aquiculture sewerage is removed and is being aerated
During the flocculent deposit that produces, while adsorb cation unnecessary in water, remove unnecessary Strong oxdiative material, make aquaculture
Sewage reverts to the state of approximate natural water body, and the aquiculture sewerage by reduction treatment passes through flow apron a35 and water level
Baffle a32 flows into catch basin a30, and the aquiculture sewerage for finally completing purification reduction treatment is directly discharged into by water outlet b33
The natural waters such as river, river, lake, sea.
Further, precipitation tank 44, lautertuns 47 and catch basin b49 inside filter plant 4 are precipitated, in reduction apparatus 6
The reduction cell 25 and catch basin a30 in portion are respectively equipped with independent sewage draining exit, and sewage is directly entered rubbish by independent blow-off line
Rubbish pond, avoids sewage backflow from mutually polluting.
Further, the filter medium for precipitating the filling of 4 self-filtering groove 47 of filter plant is fine sand 48, coarse sand 56, ratio
For：5:2, divide two layers of filling from top to bottom in the order described above.
Further, the reducing medium of 6 inside reduction cell 25 of reduction apparatus filling be quartz sand 22, it is medical stone 20, porous
Carbon 19, active zeolite 36, ratio 3:2:6:4, divide four layers of filling from top to bottom in the order described above.
In order to preferably realize the object of the invention, the present invention discloses a kind of processing for aquiculture sewerage discharge again
The device therefor of method, including：Precipitate filter plant 4, cleaning equipment 5, reduction apparatus 6.
Wherein, the precipitation filter plant 4 of step A is babinet c50 structures, and the babinet c50 is by precipitation tank 44, lautertuns
47th, catch basin b49 is formed；The side of the babinet c50 is equipped with a water inlet c42, water inlet 40 of removing contamination, backwash water inlet 40
With discharge outlet 38 of removing contamination, opposite side, which is equipped with before water outlet c51, the babinet c50, is equipped with sewage draining exit d46, sewage draining exit e52, row
Dirty mouth f58；The babinet c50 is internally provided with unrestrained water baffle 45, flow apron b54 and water level baffle b53, the unrestrained water baffle 45
Between precipitation tank 44 and lautertuns 47, the flow apron b54 and water level baffle b53 are located at lautertuns 47 and catch basin
Between b49；44 bottom of precipitation tank is form of pot bottom, and the circumferential bottom centre in bottom four tilts, and bottom centre is equipped with central row
Dirty mouth 59, the bottom are surrounded by nozzle 41 of removing contamination；44 top of precipitation tank is equipped with water spray duckbilled 43, the water spray duckbilled
43 connect with water inlet c42；47 lower part of lautertuns was equipped with water-bed plate 55, and filling filtering on the excessively water-bed plate 55 is situated between
Matter；Cross between water-bed plate 55 and filter medium and bury backwash water pipe 57.The sewage draining exit d46 is located at 47 front upper of lautertuns,
The sewage draining exit f58 is located at 47 front bottom of lautertuns；The sewage draining exit e52 is located at catch basin b49 front bottoms, the water outlet
Mouth c51 is located at mono- side bottoms of catch basin b49.
Further, the filter medium of filling is coarse sand 56 and fine sand 48 in the lautertuns 47.
Further, the backwash water pipe 57 in the lautertuns 47 carries out automatic backflushing to automatically control to filter medium
Cleaning, when 47 sluggish flow of lautertuns, starts automatic backwash, pressure pump 7 automatically turns on, and clear water passes through pressure pump 7
Backwash water pipe 57 is entered by backwash water inlet 39 after pressurization, the coarse sand 56 in lautertuns 47 and fine sand 48 are carried out reversely clear
Wash, the sewage for cleaning generation is discharged from sewage draining exit d46.
Further, the nozzle 41 of removing contamination of 44 bottom of precipitation tank is to automatically control, and the dirt of bottom is carried out automatically
Rinse, when 44 bottom dirt of precipitation tank reaches certain thickness, start automatic pollutant removal, pressure pump 7 automatically turns on, and clear water passes through
Nozzle 41 of removing contamination is entered by water inlet 40 of removing contamination after the pressurization of pressure pump 7, the bottom of precipitation tank 44 is cleaned, and is formed
Water vortex, makes dirt flow into center sewage draining exit 59, discharge outlet 38 is discharged by removing contamination.
Further, when the lautertuns 47 and catch basin b49 of cleaning precipitation filter plant 4, sewage is from the lautertuns
The sewage draining exit e52 discharges of sewage draining exit f58 and catch basin the b49 bottom of 47 bottoms.
The cleaning equipment 5 of step B is babinet a17 structures, and the babinet a17 both sides are equipped with water inlet a9 and water outlet a14；
Babinet a17 is by cation generator 10, hydroxyl radical generator 13, valve a11, valve b15, valve c16 and control module
12 compositions, the cation generator 10 are connected with hydroxyl radical generator 13 by PVC pipeline, and valve is set on the pipeline
Door c16；The hydroxyl radical generator 13 is connected with the water inlet a9 by PVC pipeline, and valve is set on the pipeline
a11；The cation generator 10 is connected with water outlet a14 by PVC pipeline, and valve b15 is set on the pipeline；The case
Fixed screw is equipped with the inside of body a17, control module 12 is fixed on the inner wall of babinet a17, and the control module 12 is by shell
80th, working power and the PLC composition being arranged in shell 80；The control module 12 is equipped with power supply indicator 79, heat dissipation
Mouth 81, manual adjustment knob 82, USB port 83 and work light 84.
When cleaning equipment 5 powers on, power supply indicator 79 lights；When cleaning equipment 5 is run, work light 84
Light；Control module 12 can be connected by the present invention by USB port 83 or WIFI with computer, and then set the operation with collecting device
Data；Especially power-off or other parameter adjustment can also be carried out by manual adjustment knob 82 in special circumstances, purification sets
When standby 5 internal temperatures are excessive, fan can be automatically turned on, the temperature of control module 12 is reduced by thermovent 81.
Cleaning equipment 5 can have four kinds of current combinations, and purified treatment is carried out to aquiculture sewerage.The first, beats
Valve opening door c16, closes valve a11 and valve b15, and aquiculture sewerage enters from bottom water inlet a9, and successively series connection is by sun
Ion generator 10 and hydroxyl radical generator 13 carry out purified treatment, are then overflowed from water outlet a14, complete the net of water body
Change process；Second, open valve b15, close valve a11 and valve c16, aquiculture sewerage from bottom water inlet a9 into
Enter, carry out purified treatment separately through cation generator 10, then overflowed from water outlet a14, complete the purification process of water body；
The third, opens valve a11, closes valve b15 and valve c16, and aquiculture sewerage enters from bottom water inlet a9, individually logical
Hydroxyl radical generator 13 carries out purified treatment, is then overflowed from water outlet a14, completes the purification process of water body；4th kind,
Valve a11 and valve b15 is opened, closes valve c16, aquiculture sewerage enters from bottom water inlet a9, while connection warp in parallel
Cross cation generator 10 and hydroxyl radical generator 13 carries out purified treatment, then overflowed from water outlet a14, complete water body
Purification process.According to aquiculture sewerage processing requirement and pollution level, can optional one of which current combination, if
Standby system default is the first current combination.
Further, the shell of the cation generator 10 by PVC groove a67 and PVC flanges a65 bond form, sun from
13 enclosure of electronic generator installs integrated Kufil electrode group 62；The copper silver ion alloy electrode group 62 is by even number
A Kufil gold plaque 63 forms, the spacing ＜ 10mm of two neighboring electrode slice；The shell of the hydroxyl radical generator 13 by
PVC groove b78 and PVC flanges b75 is bonded and formed, and 13 enclosure of hydroxyl radical generator installs integrated coated titanium electrode
Group 72；The coated titanium electrode group 72 is made of odd number coated titanium electrode piece 71, the spacing ＜ 10mm of two neighboring electrode slice.
As a preferred embodiment of the present invention, 10 both ends of cation generator are respectively provided with a PVC ring flange
61, wherein one end is equipped with a PVC disk 64；Stainless steel binding post 60 is respectively equipped with the PVC ring flanges 61 and PVC disks 64；
13 both ends of hydroxyl radical generator are respectively provided with a titanium ring flange 70, and wherein one end is equipped with a titanium dish 74；The titanium
Titanium binding post 69 is respectively equipped with ring flange 70 and titanium dish 74.
Further, the Kufil gold plaque 63 is divided to for two groups, wherein, on the PVC ring flanges 61 of one group of fixation at one end,
Another group one end is fixed on PVC disks 64；The coated titanium electrode piece 71 is divided to for fixed electrode film and extends two kinds of electrode slice,
The fixed electrode film is divided into two groups, and one end of one of which is fixed in the titanium dish 74 of side, and another group one end is fixed on
On the titanium ring flange 70 of opposite side；The fixed electrode film is odd-level, is prolonged between adjacent two panels fixed electrode film equipped with one layer
Long electrode piece, the extension electrode slice are fixed on the gap location between adjacent two panels fixed electrode film by polyamide bolt 22,
The extension electrode slice is even level.
Further, the Kufil gold plaque 63 passes through copper conductor and 60 phase of stainless steel binding post on PVC ring flanges 61
Even.
Further, by connecing between the control module 12 and cation generator 10 and hydroxyl radical generator 13
Terminal is connected with cable.
Further, connected between PVC ring flanges 60 and PVC the flanges a65 by stainless steel bolt 68；The titanium method
Connected between blue disk 70 and PVC flanges b75 by titanium bolt 77.
As a preferred embodiment of the present invention, two flowing water mouths are offered on the shell of the cation generator 10
a66.Two flowing water mouth b76 are offered on the shell of the hydroxyl radical generator 13.
The reduction apparatus 6 of step C is babinet b31 structures, and side is equipped with air inlet 24 and recoil water inlet 23, and opposite side is set
There is water outlet b33, top is equipped with water inlet b26；Flow apron a35 and water level baffle a32 is equipped with the babinet b31, by case
B31 points of body is reduction cell 25 and catch basin a30, and 25 front bottom of reduction cell is equipped with sewage draining exit a18, and front upper is equipped with row
Dirty mouth b29；Water tray 37, recoil water pipe 21, reducing medium, nanometer aeration disk 28 and spray tube were equipped with the reduction cell 25
27, the spray tube 27 is located at the top of reduction cell 25 and is connected with water inlet b26；The reducing medium was filled on water tray 37
Face, the nanometer aeration disk 28 are located above reducing medium, and the water outlet b33 is located at catch basin a30 sides, the sewage draining exit
C34 is located at catch basin a30 front bottoms.
Further, when reduction apparatus 6 is run, air pump 8 automatically turns on, and air enters nanometer aeration by air inlet 24
Disk 28, starts to carry out Air Exposure to aquiculture sewerage.
Further, the reducing medium in the reduction cell 25 is quartz sand 22, medical stone 20, porous carbon 19 and activation boiling
Mountain flour 36.
Further, the recoil water pipe 21 is arranged on 22 bottom of quartz sand, the top of medical stone 20.
Further, the backwash tube 21 in the reduction cell 25 carries out automatic backflushing to automatically control to quartz sand 22
Cleaning, when the water of reduction cell 25 flows through slow, starts automatic backwash, pressure pump 7 automatically turns on, and clear water passes through pressure pump
Recoil water pipe 21 is entered by the water inlet 23 that recoils after 7 pressurizations, reverse cleaning, cleaning are carried out to the quartz sand 22 in reduction cell 25
The sewage of generation is discharged from sewage draining exit b29.
Further, when cleaning reduction apparatus 6, sewage draining exit a18 and catch basin of the sewage from 25 bottom of reduction cell
The sewage draining exit c34 discharges of a30 bottoms.
The operation principle of the present invention is as follows：After aquiculture sewerage flows into cation generator 10, Kufil gold plaque 63 is sent out
Raw cell reaction, produces the luxuriant son of copper silver, is combined by the copper silver ion and electronegative bacterial cell of positively charged, copper silver ion
Penetration cell wall is combined with the DNA and RNA of intracellular privileged site, is destroyed the protease and respiratory enzyme of bacterial cell, is caused
The dissolving and death of bacterial cell.After aquiculture sewerage flows into hydroxyl radical generator 13, generation hydroxyl radical free radical (
OH) and other Strong oxdiative materials, hydroxyl radical free radical (OH) is because it has high oxidizing potential (2.80eV), its oxidability pole
By force, can occur quick chain reaction with most organic pollutants, non-selectivity having in aquiculture sewerage
Evil material is oxidized to CO2、H2O or mineral salt.The porous carbon filled at the same time between Ti electrode piece can improve pair in electrolytic process
The utilization rate of water intermediate ion.Copper silver ion acts synergistically with hydroxyl radical free radical (OH) and other Strong oxdiative materials, can make water
The treatment effeciency for producing aquaculture wastewater improves three times.
The present embodiment is using high frequency electric source control cation generator 10 and the power of hydroxyl radical generator 13, to water
Body processing index is accurately adjusted.The adjust automatically of equipment, temperature automatically controlled is realized by control module 12；The present invention is also set
USB port 83 is equipped with, can realize the operation of remote supervisory and control(ling) equipment to the present invention by WIFI, computer；Control module 12 is using automatic
Temperature control, waterproof, insect prevention, antirust design.Power supply in control module 12 is designed using dual power supply, a working power, one it is standby
Use power supply.When working power is problematic or power-off occurs, stand-by power supply automatically begins to work immediately, does not interfere with just
Normal sewage treatment works；By the manual adjustment knob 82 of the present invention, automatic function failure can be effectively avoided the occurrence of
Situation；Water flow by setting the present invention controls probe, realizes when can be too small or anhydrous in water and is automatically stopped equipment
Work, and then the present invention is protected, extend the service life of the present invention.
In the embodiment shown in fig. 10, in control principle drawing PLC be control module 12 core, all data will pass through
PLC is handled and is sent instruction；Data-signal is passed to PLC by automatic cleaning probe, water quality monitoring probe, traffic protection probe,
PLC passes to high frequency electric source after program is analyzed, by command signal, and the processing of PLC can be collected by WIFI and computer
Data, and instruction can be transmitted to PLC and then control and adjust the running parameter of Ti electrode；Temp probe can be controlled by PLC
The unlatching of fan processed is radiated；Automatic back-washing probe can control the unlatching of automatic back-washing device to carry out backwash work by PLC
Make；Automatic pollutant removal probe can control the unlatching of automatic dirt cleaning device to carry out work of removing contamination by PLC；Can be with by the above process
Realize the automatic cleaning of equipment, adjust automatically, automatic protection closing, temperature automatically controlled, automatic back-washing, automatic pollutant removal, can also lead to
Cross the operation of WIFI and computer remote monitoring device.
Present invention physical and chemical factor mutation analysis during certain aquatic farm is tested
In Figure 11 to Figure 14, purification reductive water is the aquiculture sewerage after equipment is handled；Aquiculture sewerage is
Not by the aquiculture sewerage of equipment processing.
A, ammonia nitrogen changes
As seen from Figure 11：Total ammonia content highest order 0.035mg/L of reductive water or so is purified, being converted into non-ionic ammonia is
0.005mg/L, less than the regulation of China water quality standard for fishery 0.02mg/L；Ammonia nitrogen removal ratio amplitude is in 65.71-87.50%
Between, ratio is averagely removed 70.09%.Illustrate that equipment removes the positive effect of ammonia nitrogen.
B, nitrite changes
As seen from Figure 12：Cultured water content is finally stablized in 0.013mg/L or so, less than China's water quality standard for fishery
The regulation of 0.1mg/L, and amplitude of variation very little.Between 51.85-59.38%, average removal rate is cultured water removal rate
54.62%.Illustrate that equipment removes the positive effect of cultured water.
C, bacterium changes
As seen from Figure 13：Equipment water outlet is average to kill to bacterial inactivation rate 92.00-100.00% in aquiculture sewerage
Rate is 96.63%.Illustrate that equipment has obvious bactericidal effect.
D, vibrios changes
As seen from Figure 14：Equipment water outlet is 96.09-100% to vibrios killing rate in aquiculture sewerage, average killing rate
For 98.4%.Illustrate that equipment kills vibrios positive effect.
Data above illustrates that the present invention can meet the index request of fish aquaculture sewage discharge completely, has reached water
The requirement of aquaculture wastewater purification reduction is produced, is adapted to the aquatic farm use in various scales, it is increasingly tight in marine environmental pollution
In the case of weight, possesses wide prospect.
The above, is only presently preferred embodiments of the present invention, not does limitation in any form to the present invention, it is every according to
According to the technical spirit of the present invention, any simply modification and equal change, each fall within guarantor of the invention to made by above example
Within the scope of shield.
Claims (10)
1. a kind of processing method for aquiculture sewerage discharge, it is characterised in that include the following steps：Step A, aquatic products is supported
The aquiculture sewerage of bottom of pond portion discharge is grown, by precipitating filter plant preliminary purification, it is insoluble to remove suspended particulate and excrement etc.
In the dirt of water；Step B, aquiculture sewerage passes through cleaning equipment, removes ammonia nitrogen, nitrite, heavy metal, antibiosis in water removal
The harmful substances such as element are simultaneously sterilized；Step C, aquiculture sewerage passes through reduction apparatus, removes impurity tiny in water removal, colloid protein
The flocculent deposit of formation, unnecessary cation and Strong oxdiative thing, the aquiculture sewerage for completing purification reduction treatment pass through water outlet
Mouth is directly discharged into the natural water bodies such as river, river, lake, sea.
2. a kind of processing method for aquiculture sewerage discharge according to claim 1, it is characterised in that step A has
Body is, aquiculture sewerage is discharged from the bottom center sewage draining exit of aquaculture pond, by water pump lifting, by water inlet c into
Enter to precipitate filter plant, primary purifying is carried out to aquiculture sewerage, water body first passes through water spray duckbilled and flows into precipitation tank, goes to remove water
In remaining bait, bulky grain suspended matter, animal wastes, the material not soluble in water such as algae of death, then by place of settling
The aquiculture sewerage of reason enters lautertuns by unrestrained water baffle, by filter media, goes tiny in water removal do not dissolve in
The material of water, the aquiculture sewerage after filtering enters catch basin b by flow apron b and water level baffle b, finally from catch basin
The water outlet c outflows of b bottoms, complete preliminary purification processing, and the dirt isolated enters garbage pool, can be with working process as plant
Thing fertilizer recycles；
Step B carries out going deep into purification specifically, enter cleaning equipment by water inlet a by the aquiculture sewerage of step A,
Cleaning equipment is made of cation generator and hydroxyl radical generator, and cation and hydroxyl free can be produced by electrolysis
The Strong oxdiative thing such as base, cation and Strong oxdiative thing synergistic effect, can more quickly and efficiently kill bacterium in water, vibrios, disease
Poison, algae, parasite, reduce aquiculture sewerage in ammonia nitrogen and content of nitrite, remove water body in soluble organic,
The harmful substance such as antibiotic and heavy metal, aquiculture sewerage successively flow through cation generator and hydroxyl radical generator,
Purified treatment is goed deep into completion, and aquiculture sewerage is flowed out by water outlet a；
Step C enters by spray tube specifically, enter reduction apparatus by water inlet b by the aquiculture sewerage of step B
Reduction cell, water body is carried out Air Exposure first in reduction cell by nanometer aeration disk, and aeration can accelerate the flocks of water body
Effect, makes tiny suspended particulate and colloid protein that aquiculture sewerage produces in step B electrolytic processes form flocculent deposit,
Then reduction treatment carries out water body by multilayer reducing medium, removal aquiculture sewerage produces cotton-shaped in aeration process
Precipitation, while cation unnecessary in water is adsorbed, unnecessary Strong oxdiative material is removed, aquiculture sewerage is reverted to approximate day
The state of right water, the aquiculture sewerage by reduction treatment flow into catch basin a by flow apron a and water level baffle a, finally
The aquiculture sewerage for completing purification reduction treatment is directly discharged into the natural waters such as river, river, lake, sea by water outlet b.
A kind of 3. processing method for aquiculture sewerage discharge according to claim 2, it is characterised in that precipitation filtering
The filter medium of equipment self-filtering groove filling is fine sand, coarse sand；The reducing medium of reduction apparatus filling is quartz sand, wheat meal
Stone, porous carbon, active zeolite.
A kind of 4. processing method for aquiculture sewerage discharge according to claim 2, it is characterised in that precipitation filtering
Reduction cell inside precipitation tank, lautertuns and catch basin b, reduction apparatus and catch basin a inside equipment are respectively equipped with independent
Sewage draining exit, sewage are directly entered garbage pool by independent blowdown old road, avoid sewage backflow from mutually polluting.
5. the equipment used in a kind of processing method for aquiculture sewerage discharge, its feature exist according to claim 2
In the precipitation filter plant of step A is babinet c structures, and the babinet c is made of precipitation tank, lautertuns, catch basin b；The case
The side of body c is equipped with a water inlet c, water inlet of removing contamination, backwash water inlet and discharge outlet of removing contamination, and opposite side is equipped with a water outlet
Sewage draining exit d, sewage draining exit e, sewage draining exit f are equipped with before mouth c, the babinet c；The box house is equipped with unrestrained water baffle, water conservancy diversion gear
Plate b and water level baffle b, the unrestrained water baffle is between precipitation tank and lautertuns, the flow apron b and water level baffle b
Between lautertuns and catch basin b；The precipitation trench bottom is form of pot bottom, and the circumferential bottom centre in bottom four tilts, in bottom
The heart is equipped with center sewage draining exit, and the bottom is surrounded by nozzle of removing contamination；The precipitation tank top is equipped with water spray duckbilled, the water spray
Duckbilled is connected with water inlet c；The lautertuns lower part was equipped with water-bed plate, and filter medium is filled on the excessively water-bed plate；Cross water
Backwash water pipe is buried between bottom plate and filter medium；The sewage draining exit d is located at lautertuns front upper, and the sewage draining exit f is located at
Lautertuns front bottom；The water outlet c is located at mono- side bottoms of catch basin b, and the sewage draining exit e is located at catch basin b front bottoms；
The cleaning equipment of step B is babinet a structures, by cation generator, hydroxyl radical generator, valve a, valve b, valve
Door c and control module composition, the babinet a both sides are equipped with water inlet a and water outlet a；The cation generator and the hydroxyl
Base free-radical generator is connected by PVC pipeline, and valve c is set on the pipeline；The hydroxyl radical generator with it is described
Water inlet is connected by PVC pipeline, and valve a is set on the pipeline；The cation generator passes through PVC with the water outlet
Pipeline connects, and valve b is set on the pipeline；Fixed screw is equipped with the inside of the babinet a, control module is fixed on the interior of babinet
On wall, the control module is made of shell, working power, stand-by power supply and the PLC of setting inside the shell；The cation hair
The shell of raw device is bonded by PVC groove a and PVC flanges a to be formed, and cation generator enclosure installs integrated Kufil
Electrode group；The copper silver ion alloy electrode group is made of even number Kufil gold plaque, the spacing ＜ of two neighboring electrode slice
10mm；The shell of the hydroxyl radical generator is bonded by PVC groove b and PVC flanges b and formed, outside hydroxyl radical generator
Integrated coated titanium electrode group is installed inside shell；The coated titanium electrode group is made of odd number coated titanium electrode piece, adjacent
The spacing ＜ 10mm of two electrode slices；
The reduction apparatus of step C is babinet b structures, and side is equipped with air inlet and recoil water inlet, and opposite side is equipped with water outlet b,
Top, which is equipped with before water inlet b, the babinet b, is equipped with sewage draining exit a, sewage draining exit b, sewage draining exit c；Water conservancy diversion is equipped with the babinet b
Baffle a and water level baffle a, by babinet, b points are reduction cell and catch basin a；The sewage draining exit a is arranged on reduction cell front bottom,
The sewage draining exit b is arranged on reduction cell front upper；Water tray, recoil water pipe, reducing medium were equipped with the reduction cell, was received
Rice aeration plate and spray tube, the spray tube is located at the top of reduction cell to be connected with water inlet b；The reducing medium was filled in water
Above pallet, the nanometer aeration disk is located above reducing medium, and the water outlet b is located at the side of catch basin a, the blowdown
Mouth c is located at the front bottom of catch basin a.
6. the equipment used in a kind of processing method for aquiculture sewerage discharge, its feature exist according to claim 5
In the cation generator both ends are respectively provided with a PVC ring flange, and the PVC ring flanges are equipped with binding post；The hydroxyl
Free-radical generator both ends are respectively provided with a titanium ring flange, and the titanium ring flange is equipped with binding post.
7. the equipment used in a kind of processing method for aquiculture sewerage discharge, its feature exist according to claim 5
In the Kufil gold plaque is fixed on PVC ring flanges；The Kufil gold plaque passes through the wiring on copper conductor and PVC flanges
Column is connected.
8. the equipment used in a kind of processing method for aquiculture sewerage discharge, its feature exist according to claim 5
In the coated titanium electrode piece is divided into fixed electrode film and extends two kinds of electrode slice, and described fixed electrode film one end is fixed on titanium
On disk, the fixed electrode film is odd-level, and one layer of extension electrode slice, the extension are equipped between adjacent two panels fixed electrode film
Electrode slice is fixed on the gap location between adjacent two panels fixed electrode film by polyamide bolt, and the extension electrode slice is even number
Layer.
9. the equipment used in a kind of processing method for aquiculture sewerage discharge, its feature exist according to claim 5
In the shell both sides of the control module are equipped with thermovent, and control module front end face is equipped with manual adjustment knob, work light
And USB port.
10. the equipment used in a kind of processing method for aquiculture sewerage discharge, its feature exist according to claim 5
In the control module is connected between cation generator and hydroxyl radical generator by binding post and cable.
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| CN201711131204.9A CN107902808A (en) | 2017-11-15 | 2017-11-15 | A kind of processing method and equipment for aquiculture sewerage discharge |
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| CN108557971A (en) * | 2018-06-19 | 2018-09-21 | 大连合众金水科技有限公司 | Integrated form purifier |
| CN109019787A (en) * | 2018-09-25 | 2018-12-18 | 河南国康实业有限公司 | Copper silver ion formula herding water disinfection equipment |
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| CN111268871A (en) * | 2020-03-31 | 2020-06-12 | 海南禄泰海洋生物科技有限公司 | Shrimp breeds sewage purification unit |
| CN111659165A (en) * | 2020-06-19 | 2020-09-15 | 广东石油化工学院 | Low-energy-consumption treatment device and treatment method for mariculture sewage |
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