CN109626521A - High-frequency impulse electrochemistry handles fluoride waste method and device thereof - Google Patents

High-frequency impulse electrochemistry handles fluoride waste method and device thereof Download PDF

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Publication number
CN109626521A
CN109626521A CN201910071843.3A CN201910071843A CN109626521A CN 109626521 A CN109626521 A CN 109626521A CN 201910071843 A CN201910071843 A CN 201910071843A CN 109626521 A CN109626521 A CN 109626521A
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waste water
area
waste
water
fluoride
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周新建
周志娟
潘丙州
彭龙
王亮亮
王厉凯
任国龙
邢孟磊
孙玉中
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Xinxiang Blue Sea Environmental Science And Technology Co Ltd
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Xinxiang Blue Sea Environmental Science And Technology Co Ltd
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/463Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrocoagulation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/467Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
    • C02F1/4672Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electrooxydation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5281Installations for water purification using chemical agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/54Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
    • C02F1/56Macromolecular compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F2001/007Processes including a sedimentation step
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/12Halogens or halogen-containing compounds
    • C02F2101/14Fluorine or fluorine-containing compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2201/00Apparatus for treatment of water, waste water or sewage
    • C02F2201/46Apparatus for electrochemical processes
    • C02F2201/461Electrolysis apparatus
    • C02F2201/46105Details relating to the electrolytic devices
    • C02F2201/4612Controlling or monitoring
    • C02F2201/46125Electrical variables
    • C02F2201/4614Current
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2201/00Apparatus for treatment of water, waste water or sewage
    • C02F2201/46Apparatus for electrochemical processes
    • C02F2201/461Electrolysis apparatus
    • C02F2201/46105Details relating to the electrolytic devices
    • C02F2201/4612Controlling or monitoring
    • C02F2201/4615Time
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2201/00Apparatus for treatment of water, waste water or sewage
    • C02F2201/46Apparatus for electrochemical processes
    • C02F2201/461Electrolysis apparatus
    • C02F2201/46105Details relating to the electrolytic devices
    • C02F2201/4616Power supply
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/005Processes using a programmable logic controller [PLC]
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/05Conductivity or salinity

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  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
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  • Chemical Kinetics & Catalysis (AREA)
  • Electrochemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

The invention discloses high-frequency impulse electrochemistries to handle fluoride waste method and device thereof, and the task of the present invention is what is completed in this way, includes the following steps;Water distributionThrough step 1 waste water adjusted, by water distribution area lower part water distributing pore even into electrochemical reaction area.Waste water after step 2 reaction, by reaction zone top even into rear reaction zone, waste water is set adequately to react in rear reaction zone, step 5, the waste water after step 4 coagulating enter settling zone by bottom, waste water is after precipitating clarification, the overflow weir standard discharge that clarified wastewater is arranged through settling zone top, the sludge being deposited in settling zone bottom pyramidal slot, is discharged by sludge pipe.The present invention has the effect that the integration apparatus of the technologies such as collection electrochemical oxidation, reduction, flocculation, and structure is simple, and occupied area is small;The abilities such as redox reaction and flocculation are stronger compared with other methods ability, and operation is controllable, stable effluent quality;Secondary pollution is few, high degree of automation, is convenient for operational administrative.

Description

High-frequency impulse electrochemistry handles fluoride waste method and device thereof
Technical field
Fluoride waste method and device thereof are handled with high-frequency impulse electrochemistry the present invention relates to a kind of, especially suitable for enterprise It is used when fluoride wastewater treatment.
Background technique
Fluoride is not only limited to bone and tooth to the toxic effect of human body, can also inhibit lipase, sclerotin phosphatase and The activity of the enzymes such as urease causes metabolism disorder, inhibits endocrine effect, generates not to gonad, adrenal gland and pancreas Good influence seriously threatens human body physical and mental health.So country has formulated more stringent standard, standard to fluoride waste discharge Provide industrial enterprise's waste water content of fluoride in 10mg/L hereinafter, drinking water content of fluoride 1.0mg/L or less.
Mainly there are chemical precipitation method, flocculation sedimentation, absorption method etc. to the method for fluoride wastewater treatment at present.It is heavy by chemistry High-concentration fluorine-containing waste water concentration can be reduced to 30mg/L or so by shallow lake method, then again through flocculation sedimentation or absorption Combined Treatment Afterwards, its concentration is made to be reduced to 10mg/L or so.But operation is excessively cumbersome, addition chemicals pharmaceutical quantities are very big, the sludge of generation And secondary pollution is more, and treatment effect is also unstable.
Patent " fluorine-contained wastewater treatment system and method " Patent No. 201610060678.8 of State Patent Office's authorization, It is characterized by comprising one section to remove fluorine ion device, and chemicals dosing plant, control device, the medicament includes calcium salt, the calcium salt energy It reacts with the fluorine ion in the fluoride waste to generate calcium fluoride precipitate, the calcium fluoride precipitate is aggregated and is sunk It lowers to carry out mud-water separation, then the fluoride waste is discharged, shortcoming is that above-mentioned processing generates sludge and two Secondary pollutant is more, and treatment effect is also unstable.
A kind of patent " fluorine-contained wastewater treatment system " Patent No. 201720296698.5 of State Patent Office's authorization, it is special Sign is: including absorption tower (1), the lower part of absorption tower (1) is provided with fluoride waste slot (11), the outlet of fluoride waste slot (11) End is by pipeline and goes out to give pump C(8) it is connect with the input end of storage pool (2), abacus (21) are set in storage pool (2), orifice plate (21) be provided with below strainer (22), the outlet end of storage pool (2) by pipeline and go out give pump B(7) and reaction tank (3) a left side The connection of side-entrance end, the right side input end of reaction tank (3) is by pipeline and goes out to give pump A(6) outlet end company with adsorption tank (4) It connects, the outlet at bottom end of reaction tank (3) is connect by pipeline with sedimentation basin (5), and the two sides of reaction tank (3) are provided with heating device (9), heating device (9) is provided with computer heating control case (10).Present treatment system is the orifice plate and strainer by being arranged in storage pool, Solid pollutant is filtered, then its shortcoming is this place by the reactivity of heating device in reaction tank raising mixed liquor It is big to manage system structure layout area occupied, and mixed liquor mainly uses ingredient for anionic polyacrylamide, it is processed useless The standard of drinking water is not achieved in water.
Summary of the invention
The task of the present invention is the mass concentrations for proposing a kind of treated fluoride waste remnants fluorine ion can reach country Defined discharge standard or drinking water standard.
The task of the present invention is what is completed in this way, it is characterised in that: includes the following steps;
Fluoride waste to be processed is injected water distribution area by waste water pump, added in water distribution area by step 1, water distribution according to wastewater treatment capacity Adding sodium hydroxide solution or sulfuric acid solution adjust waste water pH value, adjust conductivity of waste water in water distribution area addition sodium chloride solution;
Step 2, through step 1 waste water adjusted, by water distribution area lower part water distributing pore even into electrochemical reaction area.It is anti-in electricity Under the action of the positive and negative pole plate direct current for answering area, metal ion forms various hydroxyl complexings through hydrolysis, polymerization, oxidation and reduction Object, multinuclear hydroxo complex make fluoride form wadding body in its stable form, according to waste water quality and row down to hydroxide Standard is put, the electrochemical reaction time is 5-20 min;
Step 3, the waste water after step 2 reaction obtain waste water in rear reaction zone by reaction zone top even into rear reaction zone Adequately to react, the rear reaction time is 3-10 min;
Step 4, the waste water reacted after step 3 the reaction zone bottom after enter coagulating area.In coagulating area, addition is helped Solidifying agent PAM strengthens the flocculating effect and rapid precipitation performance of wadding body in waste water, and the coagulating area residence time is 2-3min;
Step 5, the waste water after step 4 coagulating enter settling zone by bottom, and waste water is after precipitating clarification, clarified wastewater The overflow weir standard discharge being arranged through settling zone top, the sludge being deposited in settling zone bottom pyramidal slot, passes through sludge pipe Discharge.In step 1, added sodium hydroxide solution or sulfuric acid solution are subject to the fluorine-containing pH value of waste water in 6.5-8.5;It is added Sodium chloride solution makes the conductivity of waste water between 20000-40000 μ S/cm.In step 2, according to waste water content of fluoride And discharge standard, the electrode plate high-frequency pulse voltage in electrochemical reaction area are 8~12V;Electrode plate current density is 60-110A/ M2, high frequency pulse power supply duty ratio are 50-80%, and high-frequency electrical pulses source frequency is 2500Hz.In step 4, the hybrid reaction area Mixed form be that baffling is hybrid, by the mixing of above and below waste water and left and right disengaging, make added flocculation aid and waste water With the reaction of abundant mixing.In step 4, added flocculation aid is anion PAM, and additive amount is that 0.2%, PAM of wastewater flow rate dilutes Concentration 0.1%.In steps of 5, settling zone surface loading is 3.0m3/m2.h.
Device in a kind of high-frequency impulse electrochemistry processing fluoride waste method, it is characterised in that: box house partition Successively by water distribution area, electrochemical reaction area, rear reaction zone, coagulating area, settling zone are separated as independent unit, the electricity The rear reaction zone that chemical reaction zone is distributed below is connected with the water inlet of the water distribution area of head end by circulation line, the circulation pipe It is connected with circulating pump among road and constitutes circulation in waste water, the rear reaction zone bottom, which is provided with to be discharged, enters coagulating area, then into Entering settling zone precipitating, the settling zone top is provided with inclined plate packing, the waste water outflow weir plate that waste water is arranged by settling zone top, And be discharged by water outlet, the water outlet is arranged in the top of settling zone and is discharged by pipeline, and mud discharging mouth setting is precipitating Area side, and sludge pipe is connected on mud discharging mouth.The partition uses PE plate, and the water distribution area cabinet, bottom is provided with draining Slot, and the slot bottom of rhone is uniformly machined with drainage hole, the settling zone bottom is pyramidal structure.The electric flocculation reaction zone case There are anode plate and cathode plate according to a fixed spacing alternating sequence in vivo, and the wiring of anode plate is drawn by the way that copper bar connection is simultaneously outer It is connect with high frequency pulse power supply anode, and the wiring of cathode plate is connected by copper bar, and draws connect with high frequency pulse power supply cathode outside It connects.The spacing of the yin, yang pole plate is 20mm-30mm, the preferential aluminium sheet of yin, yang pole plate, with a thickness of 8mm.
The present invention has the effect that
1, the present invention is the integration apparatus for collecting the technologies such as electrochemical oxidation, reduction, flocculation, and structure is simple, and occupied area is small;
2, the abilities such as redox reaction and flocculation are stronger compared with other methods ability, and operation is controllable, stable effluent quality;
3, operating parameter, flexible operation can be adjusted according to processing waste water water and water quality;
4, it is not required to addition chemical agent, secondary pollution is few;
5, the device is controlled using PLC or controller, high degree of automation, is convenient for operational administrative.
Detailed description of the invention
Fig. 1 is the structural schematic diagram of present invention processing waste water fluorine processing unit;Fig. 2 is present invention processing waste water fluorine processing dress Set sewage treatment flow graph.
Drawing explanation: 1, water distribution area, 2, electrochemical reaction area, 3, rear reaction zone, 4, coagulating area, 5, settling zone, 6, Inclined plate packing, 7, overflow weir, 8, water inlet pipe, 9, circulating water pipe, 10, outlet pipe, 11, cathode plate, 12, anode plate, 13, circulation Water pump, 14, sludge pipe, 15, cabinet.
Specific embodiment
The embodiment of the present invention is described below in detail, examples of the embodiments are shown in the accompanying drawings, wherein from beginning to end Same or similar label indicates same or similar element or element with the same or similar functions.Below with reference to attached The embodiment of figure description is exemplary, it is intended to is used to explain the present invention, and is not considered as limiting the invention.
The electrochemical process for treating of fluoride waste is under the action of direct current, and anode generates metal ion, is hydrolyzed, is gathered It closes, aoxidize and restores, form various hydroxo complexes, multinuclear hydroxo complex down to hydroxide, make the pollutant in electric field It is combined into solid particle in its stable form with ionization product, the precipitation and separation from waste water.The electrochemical reaction has simultaneously The characteristics of oxidation, reduction, ion exchange, absorption and complexing flocculation.
The device of processing fluoride waste includes cabinet, with partition successively by water distribution area 1, electrochemical reaction area inside cabinet 15 2, rear reaction zone 3, coagulating area 4, settling zone 5 are separated as independent unit, and the partition uses PE plate, the electrochemistry The water inlet 8 of the water distribution area 1 of rear reaction zone 3 and head end that reaction zone 2 is distributed below is connected by circulation line 9, the circulation It is connected with circulating pump 13 among pipeline and constitutes circulation in waste water, the purpose is to improve the water velocity of reaction zone, improves mixability, Strengthen reaction efficiency, reduces energy consumption.The rear reaction zone bottom is provided with apopore and enters coagulating area 4, enters back into Settling zone 5 precipitates, and the settling zone top is provided with inclined plate packing 6, the waste water outflow weir plate that waste water is arranged by settling zone top 7, and be discharged by water outlet, the water outlet 10 is arranged in the top of settling zone and is discharged by pipeline, and mud discharging mouth setting exists Settling zone side, and sludge pipe 14 is connected on mud discharging mouth.
The water distribution area cabinet, bottom is provided with rhone, and the slot bottom of rhone is uniformly machined with drainage hole.
There are anode plate 11 and cathode plate 12 according to a fixed spacing alternating sequence in the electric flocculation reaction zone cabinet, and The wiring of anode plate is connect by drawing outside copper bar connection simultaneously with high frequency pulse power supply anode, and the wiring of cathode plate passes through copper bar and connects It connects, and draws connect with high frequency pulse power supply cathode outside, the spacing of the yin, yang pole plate is 20mm-30mm, the yin, yang pole plate Preferential aluminium sheet, with a thickness of 8mm.
5 bottom of settling zone is pyramidal structure, the inclined plate packing of top setting, it is therefore an objective to increase waste water filtering face Product reduces settling zone area, enhances sedimentation effect.
According to wastewater treatment capacity, waste water content of fluoride and discharge standard, the residence time in electric flocculation reaction zone is designed Residence time for 5-20min, rear reaction zone is designed according to 1/2 time in electrochemical reaction area.
The DC power supply that the technical program uses to reduce concentration polarization, reduces power consumption, increases for high-frequency impulse regulated power supply It adds some points the service life hit, and high-frequency impulse regulated power supply frequency is 2000-3000Hz, and high-frequency impulse regulated power supply duty ratio It is continuously adjustable for 100%, and have automatic reverse function.
Fluorine-containing waste water processing apparatus, waste water initially enter water distribution area, and water distribution area is equal by the apopore of bottom processing in slot Weighing apparatus enters electrochemical reaction area 2, and under the action of pole plate direct current, metal ion is hydrolyzed fluoride waste, polymerization, aoxidizes and goes back Original forms various hydroxo complexes, multicore hydroxyl conjunction object down to hydroxide, fluoride is made to form wadding in its stable form Body, according to waste water quality discharge standard, reaction time of the fluoride waste in electrochemical reaction area is 5-20min, containing after reaction Fluorine waste water enters rear reaction zone by electrochemical reaction area top, so that fluoride waste is adequately reacted in rear reaction zone, rear anti- The reaction time for answering area is 3-10min, and the fluoride waste of rear reaction zone enters coagulating area by rear reaction zone bottom, and to mixed Solidifying reaction zone adds flocculation aid PAM, it is therefore an objective to strengthen the flocculating effect of wadding body and rapid precipitation performance, coagulating area in waste water Residence time is 2-3min.Fluoride waste enters settling zone by coagulating area bottom, after settling zone precipitating clarification, by precipitating The overflow weir of area top setting reaches discharge standard, is discharged by discharge outlet by pipeline, the sludge of precipitating passes through mud discharging mouth Discharge.
Wherein, pass through piping connection between rear reaction zone and water distribution area, the circulating pump connected between pipeline, waste water is by rear anti- It answers the water outlet in area by pipeline, the waste water after reaction is entered into water distribution area by water inlet by circulating pump and carries out reaction again Reason, to realize circulation in reaction, the purpose is to opposite raising waste water in the water velocity of reaction zone, improve waste water and mix journey Degree strengthens reaction efficiency, reduces energy consumption, and circulating pump inner recirculation flow amount is 1-3 times for the treatment of capacity.
Using high-frequency impulse electrochemistry handle fluoride waste method the following steps are included:
Step 1;Fluoride waste to be processed is injected water distribution area by waste water pump, added in water distribution area by water distribution according to wastewater treatment capacity Adding sodium hydroxide solution or sulfuric acid solution adjust waste water pH value, adjust conductivity of waste water in water distribution area addition sodium chloride solution.
Step 2, through step 1 waste water adjusted, by water distribution area lower part water distributing pore even into electrochemical reaction area.In electricity Under the action of the positive and negative pole plate direct current for learning reaction zone, metal ion forms various hydroxyls through hydrolysis, polymerization, oxidation and reduction Complex compound, multinuclear hydroxo complex make fluoride form wadding body in its stable form, according to waste water quality down to hydroxide And discharge standard, electrochemical reaction time are 5-20 min;
Step 3, the waste water after step 2 reaction obtain waste water in rear reaction zone by reaction zone top even into rear reaction zone Adequately to react, the rear reaction time is 3-10 min;
Step 4, the waste water reacted after step 3 the reaction zone bottom after enter coagulating area.In coagulating area, addition is helped Solidifying agent PAM strengthens the flocculating effect and rapid precipitation performance of wadding body in waste water, and the coagulating area residence time is 2-3min;
Step 5, the waste water after step 4 coagulating enter settling zone by bottom, and waste water is after precipitating clarification, clarified wastewater The overflow weir standard discharge being arranged through settling zone top, the sludge being deposited in settling zone bottom pyramidal slot, passes through sludge pipe Discharge.
In step 1, added sodium hydroxide solution or sulfuric acid solution make waste water pH value between 6.5-8.5;It is added Sodium chloride solution makes the conductivity of waste water between 20000-40000 μ S/cm.
In step 2, according to waste water content of fluoride and discharge standard, the electrode plate high-frequency electrical pulses in electrochemical reaction area Pressure is 8~12V;Electrode plate current density is 60-110A/m2, and high frequency pulse power supply duty ratio is 50-80%, high frequency pulse power supply Frequency is 2500Hz.
In step 4, the mixed form in the hybrid reaction area is that baffling is hybrid, is passed in and out by above and below waste water and left and right Mixing, make reacting with abundant mixing for added flocculation aid and waste water.
In step 4, added flocculation aid is anion PAM, and additive amount is 0.2%, the PAM diluted concentration of wastewater flow rate 0.1%。
In steps of 5, settling zone surface loading is 2.0-3.0m3/m2.h.
Embodiment 1
The electrochemical reaction time is 5min in step 2, and rear reaction time 20min, added sodium hydroxide solution or sulfuric acid are molten Liquid is subject to the fluorine-containing pH value of waste water 6.5;Added sodium chloride solution makes the conductivity of waste water in 20000 μ S/cm.
In step 2, according to waste water content of fluoride and discharge standard, the electrode plate high-frequency electrical pulses in electrochemical reaction area Pressure is 8V;Electrode plate current density is 60A/m2, and high frequency pulse power supply duty ratio is 50%, and high-frequency electrical pulses source frequency is 2500Hz。
In step 4, the mixed form in the hybrid reaction area is that baffling is hybrid, is passed in and out by above and below waste water and left and right Mixing, make reacting with abundant mixing for added flocculation aid and waste water, coagulating area residence time 2min.
In step 4, added flocculation aid is anion PAM, and additive amount is 0.2%, the PAM diluted concentration of wastewater flow rate 0.1%。
In steps of 5, settling zone surface loading is 3.0m3/m2.h.
Embodiment 2
The electrochemical reaction time is 10min in step 2, and the rear reaction time is 5min, in step 1, added sodium hydroxide Solution or sulfuric acid solution are with the fluorine-containing pH value of waste water 7.5;Added sodium chloride solution makes the conductivity of waste water in 30000 μ S/ cm。
In step 2, according to waste water content of fluoride and discharge standard, the electrode plate high-frequency electrical pulses in electrochemical reaction area Pressure is 10V;Electrode plate current density is 80A/m2, and high frequency pulse power supply duty ratio is 60%, and high-frequency electrical pulses source frequency is 2500Hz。
In step 4, the mixed form in the hybrid reaction area is that baffling is hybrid, is passed in and out by above and below waste water and left and right Mixing, make reacting with abundant mixing for added flocculation aid and waste water, coagulating area residence time 2.5mi.
In step 4, added flocculation aid is anion PAM, and additive amount is 0.2%, the PAM diluted concentration of wastewater flow rate 0.1%。
In steps of 5, settling zone surface loading is 2.5m3/m2.h.
Embodiment 3
The electrochemical reaction time is 20min in step 2, and rear reaction time 10min, in step 1, added sodium hydroxide is molten Liquid or sulfuric acid solution are with the fluorine-containing pH value of waste water 8.5;Added sodium chloride solution makes the conductivity of waste water in 40000 μ S/cm.
In step 2, according to waste water content of fluoride and discharge standard, the electrode plate high-frequency electrical pulses in electrochemical reaction area Pressure is 12V;Electrode plate current density is 110A/m2, and high frequency pulse power supply duty ratio is 80%, and high-frequency electrical pulses source frequency is 2500Hz。
In step 4, the mixed form in the hybrid reaction area is that baffling is hybrid, is passed in and out by above and below waste water and left and right Mixing, make reacting with abundant mixing for added flocculation aid and waste water, coagulating area residence time 3min.
In step 4, added flocculation aid is anion PAM, and additive amount is 0.2%, the PAM diluted concentration of wastewater flow rate 0.1%。
In steps of 5, settling zone surface loading is 3.0m3/m2.h.
The present invention integrates electrochemical oxidation reactions, reduction reaction, ion exchange and flocculation sedimentation technology, thus Realize to the advanced treating of fluoride waste, effluent quality reach industrial enterprise's content of fluoride of country's formulation 10mg/L with Under, drinking water content of fluoride 1.0mg/L standard requirements below.
In the present invention unless specifically defined or limited otherwise, the arts such as term " installation ", " connected ", " connection ", " fixation " Language shall be understood in a broad sense, for example, it may be fixedly connected, may be a detachable connection or integrally connected, can be two members Connection inside part.For those skilled in the art, above-mentioned term can be understood of the invention as the case may be Concrete meaning.

Claims (10)

1. high-frequency impulse electrochemistry handles fluoride waste method and device thereof, it is characterised in that: include the following steps;
Fluoride waste to be processed is injected water distribution area by waste water pump, added in water distribution area by step 1, water distribution according to wastewater treatment capacity Adding sodium hydroxide solution or sulfuric acid solution adjust waste water pH value, adjust conductivity of waste water in water distribution area addition sodium chloride solution;
Step 2, through step 1 waste water adjusted, by water distribution area lower part water distributing pore even into electrochemical reaction area;It is anti-in electricity Under the action of the positive and negative pole plate direct current for answering area, metal ion forms various hydroxyl complexings through hydrolysis, polymerization, oxidation and reduction Object, multinuclear hydroxo complex make fluoride form wadding body in its stable form, according to waste water quality and row down to hydroxide Standard is put, the electrochemical reaction time is 5-20 min;
Step 3, the waste water after step 2 reaction obtain waste water in rear reaction zone by reaction zone top even into rear reaction zone Adequately to react, the rear reaction time is 3-10 min;
Step 4, the waste water reacted after step 3 the reaction zone bottom after enter coagulating area;
Flocculation aid PAM is added in coagulating area, strengthens the flocculating effect and rapid precipitation performance of wadding body in waste water, coagulating Area's residence time is 2-3min;
Step 5, the waste water after step 4 coagulating enter settling zone by bottom, and waste water is after precipitating clarification, clarified wastewater The overflow weir standard discharge being arranged through settling zone top, the sludge being deposited in settling zone bottom pyramidal slot, passes through sludge pipe Discharge.
2. high-frequency impulse electrochemistry according to claim 1 handles fluoride waste method and device thereof, it is characterised in that: In step 1, added sodium hydroxide solution or sulfuric acid solution are subject to the fluorine-containing pH value of waste water in 6.5-8.5;Added sodium chloride Solution makes the conductivity of waste water between 20000-40000 μ S/cm.
3. high-frequency impulse electrochemistry according to claim 1 handles fluoride waste method and device thereof, it is characterised in that: In step 2, according to waste water content of fluoride and discharge standard, the electrode plate high-frequency pulse voltage in electrochemical reaction area is 8~ 12V;Electrode plate current density is 60-110A/m2, and high frequency pulse power supply duty ratio is 50-80%, and high-frequency electrical pulses source frequency is 2500Hz。
4. high-frequency impulse electrochemistry according to claim 1 handles fluoride waste method and device thereof, it is characterised in that: In step 4, the mixed form in the hybrid reaction area is that baffling is hybrid, by the mixing of above and below waste water and left and right disengaging, is made Added flocculation aid is reacted with waste water with abundant mixing.
5. high-frequency impulse electrochemistry according to claim 1 handles fluoride waste method and device thereof, it is characterised in that: In step 4, added flocculation aid is anion PAM, and additive amount is 0.2%, the PAM diluted concentration 0.1% of wastewater flow rate.
6. high-frequency impulse electrochemistry according to claim 1 handles fluoride waste method and device thereof, it is characterised in that: In step 5, settling zone surface loading is 3.0m3/m2.h.
7. a kind of device of high-frequency impulse electrochemistry processing fluoride waste, it is characterised in that: box house is with partition successively by cloth Pool, electrochemical reaction area, rear reaction zone, coagulating area, settling zone are separated as independent unit, the electrochemical reaction The rear reaction zone that area is distributed below is connected with the water inlet of the water distribution area of head end by circulation line, is connected among the circulation line There is circulating pump to constitute circulation in waste water, the rear reaction zone bottom is provided with water outlet and enters coagulating area, enters back into settling zone Precipitating, the settling zone top is provided with inclined plate packing, the waste water outflow weir plate that waste water is arranged by settling zone top, and passes through and Mouth of a river discharge, the water outlet are arranged in the top of settling zone and are discharged by pipeline, and mud discharging mouth is arranged in settling zone side, and Sludge pipe is connected on mud discharging mouth.
8. the device of high-frequency impulse electrochemistry processing fluoride waste according to claim 7, it is characterised in that: the partition Using PE plate, the water distribution area cabinet, bottom is provided with rhone, and the slot bottom of rhone is uniformly machined with drainage hole, described Settling zone bottom is pyramidal structure.
9. the device of high-frequency impulse electrochemistry processing fluoride waste according to claim 7, it is characterised in that: the electricity wadding There are anode plate and cathode plate according to a fixed spacing alternating sequence in solidifying reaction zone cabinet, and the wiring of anode plate passes through copper bar Connect and it is outer draw connect with high frequency pulse power supply anode, and the wiring of cathode plate is by copper bar connection, and draws outside and high-frequency impulse Power cathode connection.
10. the device of high-frequency impulse electrochemistry processing fluoride waste according to claim 7, it is characterised in that: the yin, The spacing of anode plate is 20mm-30mm, the preferential aluminium sheet of yin, yang pole plate, with a thickness of 8mm.
CN201910071843.3A 2019-01-25 2019-01-25 High-frequency impulse electrochemistry handles fluoride waste method and device thereof Pending CN109626521A (en)

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