CN203715425U - Equipment for treating RO (reverse osmosis) concentrated liquid by pulse electrolysis - Google Patents

Equipment for treating RO (reverse osmosis) concentrated liquid by pulse electrolysis Download PDF

Info

Publication number
CN203715425U
CN203715425U CN201420035405.4U CN201420035405U CN203715425U CN 203715425 U CN203715425 U CN 203715425U CN 201420035405 U CN201420035405 U CN 201420035405U CN 203715425 U CN203715425 U CN 203715425U
Authority
CN
China
Prior art keywords
pond
pulse electrolysis
fenton
level settling
pulse
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Withdrawn - After Issue
Application number
CN201420035405.4U
Other languages
Chinese (zh)
Inventor
王服群
张智良
李闪
查振林
董有
熊昌贵
李徐立
郑佶
宁俊萍
王小文
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Sinosteel Wuhan Safety & Environmental Protection Research Institute Co Ltd
Original Assignee
Sinosteel Wuhan Safety & Environmental Protection Research Institute Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Sinosteel Wuhan Safety & Environmental Protection Research Institute Co Ltd filed Critical Sinosteel Wuhan Safety & Environmental Protection Research Institute Co Ltd
Priority to CN201420035405.4U priority Critical patent/CN203715425U/en
Application granted granted Critical
Publication of CN203715425U publication Critical patent/CN203715425U/en
Anticipated expiration legal-status Critical
Withdrawn - After Issue legal-status Critical Current

Links

Abstract

The utility model relates to equipment for treating a reverse osmosis (or nanofiltration) concentrated liquid of a sewage treatment system by adopting the pulse electrolysis technology. The equipment comprises a Fenton pre-treatment pool 2, a primary settling pond 7, a pulse electrolysis pond 9 and a secondary settling pond 15, wherein the Fenton pre-treatment pool 2 is internally provided with an undersurface stirrer 4, a return pump 5, a Fenton reagent guide pipe 3, and an acid adding device 18, an alkali adding device 19 and a Fenton reagent device 20 are arranged on the Fenton pre-treatment pool 2. The pulse electrolysis pond 9 is internally provided with positive and negative electrodes 10 which are connected with a pulsed power supply 12 and an oscilloscope, and a return pump 11 and an undersurface stirrer 13 are arranged inside the pulse electrolysis pond 9. An electromagnetic generator 16 is installed in the outer layer of a mud discharge bucket of the secondary settling pond 15. The utility model provides technically feasible and economically applicable reverse osmosis (or nanofiltration) concentrated liquid equipment which can be applied to engineering.

Description

The equipment of RO concentrated solution is processed in a kind of pulse electrolysis
Technical field
The utility model belongs to water and pollutes processing technology field, is specifically related to a kind of equipment that adopts pulse electrolysis technology to remove Sewage treatment systems reverse osmosis (or nanofiltration) concentrated solution.
Background technology
In recent years, reverse osmosis technology is obtaining important application in the wastewater treatment of the industries such as municipal effluent, refuse landfill, plating, printing and dyeing, Iron And Steel Industry, chemical industry, food and pharmacy or reuse.Reverse osmosis technology, in obtaining approximately 70% qualified reuse water, by concentrated approximately 3 times of the pollution substance in ultrafiltration water outlet, produces approximately 30% RO dope.As concentrated in pollutent height in percolate dope, high (the wherein CL of saltiness -be 2400 ~ 2800 mg/L), hardness is large, and COD is about 1800 ~ 2400mg/L, NH 3-N is between the mg/L of 40mg/L ~ 65, and B/C is less than 0.1, and colourity is much larger than 100 times.Traditional water technology head it off effectively, mostly enters municipal sewage pipe network and enters sanitary sewage disposal factory and office reasons or return and be sprayed onto refuse landfill, a difficult problem that is treated as environmental improvement for RO dope.
The research report of concentrated solution processing mode mainly contains chemical oxidation, fractionation by adsorption, materialization coagulation, wet oxidation, land law (returning spray containing landfill yard), photochemical catalytic oxidation, electricity-Fenton, electrochemical oxidation, the cultivation of features bacterium etc.
Pulse electrolysis is a kind of mode of electrochemical oxidation degradation of contaminant, and by constantly the process of electrode repetition " power supply-power-off-power supply " being reached to the speed that promotes redox, mass transfer, adsorption and desorption, electrolytic efficiency improves.But when single use pulse electrolysis technical finesse RO concentrated solution, electrolysing period is long, energy consumption is large, and contaminant removal efficiency is not high, and water outlet can not reach emission standard.
The purpose of this utility model is the problem high for RO concentrated solution saltiness, pollutant component is complicated, intractability is large, and pulse electrolysis technical finesse RO a kind of equipment of concentrated solution is provided.
Technical solution of the present utility model is Fenton pre-treatment, the settling apparatus that produces synergistic pulse electrolysis and attached magnetic and the method adopting with internal reflux facility, makes COD, NH 3the pollutent such as-N, colourity is effectively degraded, effluent quality reach GB require time, electric energy consumption significantly reduces.
The equipment of RO concentrated solution is processed in a kind of pulse electrolysis that the utility model provides, comprise Fenton pretreatment pool, one-level settling tank, pulse electrolysis pond, second-level settling pond, Fenton pretreatment pool is connected by pipeline with one-level settling tank, one-level settling tank connects pulse electrolysis pond by delivery pump pipe, and pulse electrolysis pond connects second-level settling pond by pipeline.
Agitator, reflux pump, fenton reagent ingress pipe under liquid is installed in described Fenton pretreatment pool, and pond body is installed online ionic concn (CL around -ion) meter, pH meter, conductivitimeter, on the body of pond, establish acid adding device, adder-subtractor, Fenton reagent device.
In described pulse electrolysis pond, positive and negative electrode is housed, is titanium electrode, electrode connects the pulse power and oscilloscope, and mixing pump under phegma is set in pulse electrolysis pond, and pond body is installed turbidimeter, pH meter, electrical conductivity meter, thermometer around.
Described second-level settling pond, at the outer electromagnetic field generator of installing of second-level settling pond mud-removing bucket.Electromagnetic field generator is that end portion coil is dense by the ring-type cone magnetic gonosome of coil winding, and upper end portion coil is sparse, electromagnetic field generator external source switch.
The operation of unit equipment is implemented to integrated module, and the equipment of being convenient to is installed, debugging and safeguarding, makes the operation of integrated artistic equipment and management simple and convenient.
The utility model adopts a kind of pulse electrolysis of described equipment to process the method for RO concentrated solution, and its technical process is: RO concentrated solution → Fenton pretreatment pool → one-level settling tank → pulse electrolysis pond → second-level settling pond → qualified discharge, concrete steps are as follows.
1. RO concentrated solution enters Fenton pretreatment pool by pipeline, and part surface promoting agent, jelly, the CL in RO concentrated solution removed in Fenton reaction -, the solution after reaction is that weakly alkaline enters one-level settling tank precipitation through adjust pH.
2. enter pulse electrolysis pond from the supernatant liquor of one-level settling tank, pulse electrolysis adds Fe in pond 3o 4, carry out electrolysis.Fe 3o 4the processing condition of collaborative pulse electrolysis are: Fe 3o 4add-on is at 1 ~ 3g/L, battery lead plate spacing approximately 1.5 ~ 3.0 ㎝, current density 5 ~ 15 mA/㎝ 2, electrolytic reaction time 20 ~ 35min, electrolyzer temperature: normal temperature ~ approximately 15 DEG C, specific conductivity 7 ~ 14 k μ S/cm rise.Fe in reaction process 3o 4constantly the small flco in absorption electrolyzer becomes compared with big flocculating body, and the pollutent in this class flco needn't participate in electrolysis and reach the object of degraded, but is deposited in second-level settling pond, exists generation very little with the form of solid, or solidifies or burn.
3. pulse electrolysis pond mixed solution out enters second-level settling pond, and electromagnetic field generator energising produces magnetic field, and magnetic force is to Fe 3o 4be adsorbed to second-level settling pond bottom, with Fe 3o 4the flco adhering to arrives the bottom of second-level settling pond, Fe 3o 4mud is discharged second-level settling pond, and supernatant liquor is Clear & Transparent, Fe 3o 4mud reclaims Fe 3o 4recycle.
The beneficial effects of the utility model: for the feature of RO concentrated solution, by chemistry redox and electrochemistry combination, adopt Fe 3o 4collaborative pulse electrolysis technology, compared with Sing plus electrolysis tech, advantage of the present utility model is as follows:
(1) pretreatment unit utilizes Fenton reaction to remove part CL in sewage -(original liquid concentration is 2200 ~ 2500mg/L, after Fenton reaction, is 900 ~ 1500mg/L), has avoided CL -react at electrode: 2CL --2e → CL 2, the CL of generation 2in the aqueous solution, react CL 2+ 2e → 2CL -, produce CL -again on electrode, react 2CL --2e → CL 2circulating reaction and produce energy consumption, make electric energy be directly used in degraded COD.
(2) Fe 3o 4work in coordination with the effect of pulse electrolysis, broken the structure of RO concentrated solution pollutent water-soluble (or dispersed), become suspension liquid, Fe 3o 4adsorb tiny suspensoid and become larger particles.The magnetic field that when energising, coil produces is by Fe 3o 4and the suspended substance of absorption is drawn to mutually settling tank bottom and becomes glaur, while having avoided electrolysis, spend in the energy consumption of fine suspension, working cost is saved.
(3) the utility model provides a kind of feasible, Processes and apparatus of being suitable for economically, can applying in engineering technically.
Brief description of the drawings
Fig. 1 is equipment structure chart of the present utility model.
Fig. 2 is to be process flow sheet of the present utility model.
Fig. 3 uses the utility model art breading percolate RO concentrated solution Inlet and outlet water Parameter Map.
Fig. 4 uses the utility model art breading tobacco sheet wastewater RO concentrated solution Inlet and outlet water Parameter Map.
In figure: 1. water-in; 2. Fenton pretreatment pool; 3. Fenton reagent ingress pipe; 4. agitator under liquid; 5. reflux pump; 6. pipeline; 7. one-level settling tank; 8. transferpump; 9. pulse electrolysis pond; 10. electrode; 11. reflux pumps; 12. pulse powers; Agitator under 13. liquid; 14. pipelines; 15. second-level settling ponds; 16. electromagnetic field generators; 17. power switches; 18. acid adjustment devices; 19. adjust alkali device; 20. Fenton reagent devices.
Embodiment
Below in conjunction with accompanying drawing, the utility model is described further.
The equipment of RO concentrated solution is processed in a kind of pulse electrolysis, comprise Fenton pretreatment pool 2, one-level settling tank 7, pulse electrolysis pond 9, second-level settling pond 15, Fenton pretreatment pool 2 is connected by pipeline 6 with one-level settling tank 7, one-level settling tank 7 connects pulse electrolysis pond 9 by transferpump 8, pulse electrolysis pond 9 connects second-level settling pond 15 by pipeline 14, agitator 4 under the interior installation liquid of Fenton pretreatment pool 2, reflux pump 5, Fenton reagent ingress pipe 3, reflux pump 5 water outlets are gondola water faucet shape, exceed liquid level, on Fenton pretreatment pool 2, establish acid adding device 18, adder-subtractor 19, Fenton reagent device 20, positive and negative electrode 10 is housed in pulse electrolysis pond 9, electrode 10 is mesh electrodes, connect the pulse power 12 and oscilloscope, pulse electrolysis pond 9 is interior arranges agitator 13 under reflux pump 11, liquid, reflux pump 11 water outlets are gondola water faucet shape, exceed liquid level, the outer electromagnetic field generator 16 of installing of second-level settling pond 15 mud-removing buckets.Electromagnetic field generator 16 is that end portion coil is dense by the ring-type cone magnetic gonosome of coil winding, and upper end portion coil is sparse, electromagnetic field generator 16 external source switches 17.
The method of RO concentrated solution is processed in a kind of pulse electrolysis, technical process is RO concentrated solution → Fenton pretreatment pool 2 → one-level settling tank 7 → pulse electrolysis pond 9 → second-level settling pond, 15 → qualified discharge, concrete steps are that 1. RO concentrated solution enters Fenton pretreatment pool 2 by water-in 1, and part surface promoting agent, jelly, the part CL in RO concentrated solution removed in Fenton reaction -, 2/3rds elevation places under reaction tank liquid introduced by Fenton reagent by Fenton reagent ingress pipe 3; Under liquid, agitator 4 makes Fenton reagent fully contact, react with pollutent; Acid adding device 18 improves Fenton reaction efficiency; The CL that reflux pump 5 produces this unit 2and other gaseous state thing is escaped.Adder-subtractor 19 makes precipitation completely, and the solution after reaction is that weakly alkaline enters one-level settling tank 7 and precipitates through adjust pH.
2. enter pulse electrolysis pond 9 from the supernatant liquor of one-level settling tank 7, in pulse electrolysis pond 9, add Fe 3o 4powder carries out electrolysis; Pulse electrolysis parameter: the interior Fe in pulse electrolysis pond 9 3o 4add-on is at 1 ~ 8g/L, electrode 10 distances between plates approximately 1.5 ~ 3.0 ㎝, current density 5 ~ 15 mA/㎝ 2, electrolytic reaction time 20 ~ 35min, pulse electrolysis pond 9 temperature: than normal temperature rise approximately 15 DEG C ~ 20 DEG C, specific conductivity 7 ~ 14 k μ S/cm; Reflux pump 11 is got rid of the CL that reaction produces 2; In the mixed solution in pulse electrolysis pond 9, add Fe 3o 4powder, Fe 3o 4attract extremely small suspended substance in electrolytic solution, and increase along with electrolysis process advances particle diameter.
3. pulse electrolysis pond 9 mixed solution out enters second-level settling pond 15, and electromagnetic field generator 16 energisings produce magnetic field, and magnetic force is to Fe 3o 4be adsorbed to second-level settling pond 15 bottoms, with Fe 3o 4the flco adhering to arrives the bottom of second-level settling pond 15, Fe 3o 4mud is discharged second-level settling pond 15, the Clear & Transparent qualified discharge of supernatant liquor, Fe 3o 4mud reclaims Fe 3o 4recycle.
Said process is by system integration module control.
Example one: process engineering RO concentrated solution as example taking somewhere, middle part consumer waste filling and embedding factory percolate, this project percolate is processed water yield 150m 3/ d, produces approximately 50 m 3the concentrated solution of/d.
Use the utility model technique Inlet and outlet water parameter to see Fig. 3:
This technical process is: 15 DEG C of Fenton pretreatment pool 2 water temperatures, reaction churning time 60min; One-level settling tank 7 comprises precipitation, spoil disposal, draining 70min altogether; Pulse electrolysis time 35min in pulse electrolysis pond 9, water temperature rises to 38 DEG C from 15 DEG C; Second-level settling pond 16 comprises electromagnetism suction precipitation, spoil disposal, water discharge time 30min altogether.
In above-mentioned technical process, Fenton pretreatment pool 2 is installed 1, useful volume 2.5m 3; One-level settling tank 7 arranges 2, each useful volume 2.5m 3; Pulse electrolysis pond 9 arranges 1, useful volume 1.8 m 3; Second-level settling pond 15 is 1, useful volume 2m 3.
In above-mentioned technical process, Fenton pretreatment pool 2, one-level settling tank 7, pulse electrolysis pond 9, second-level settling pond 15 all adopt stainless steel manufacture, and return line is pvc material; Electrode 10 adopts resin and paints anticorrosion with electric wire connection point.
System integration automatic control program in above-mentioned technical process, plant automation operation, arranges monitoring management.
This percolate RO concentrated solution is after this covering device is processed, and COD clearance can reach more than 97%, NH 3-N 98%, colourity 94%, stable water outlet reaches " integrated wastewater discharge standard " emission standard (GB8978-1996).
Example two, taking middle part tobacco sheet wastewater RO concentrated solution as example, is processed the RO concentrated solution water yield 80m every day 3.
Use the utility model technique Inlet and outlet water parameter to see Fig. 4:
This technical process is: 25 DEG C of Fenton pretreatment pool 2 water temperatures, reaction churning time 45min; One-level settling tank 7 comprises precipitation, spoil disposal, draining 70min altogether; Pulse electrolysis time 30min in pulse electrolysis pond 9,25 DEG C of water temperatures rise to 45 DEG C; Second-level settling pond 15 comprises that electromagnetism inhales precipitation, spoil disposal, water discharge time 30min altogether mutually.
In above-mentioned technical process, Fenton pretreatment pool 2 is installed 1, useful volume 3.2m 3; One-level settling tank 7 arranges 2, each useful volume 3.2m 3; Pulse electrolysis pond 9 arranges 1, useful volume 2.6 m 3; Second-level settling pond 15 is 1, useful volume 2.8m 3.
In above-mentioned technical process, Fenton pretreatment pool 2, one-level settling tank 7 arrange, pulse electrolysis pond 9, second-level settling pond 15 all adopt stainless steel manufacture; Return line is pvc material; Electrode 10 adopts resin and paints anticorrosion with electric wire connection point.
System integration automatic control program in above-mentioned technical process, makes unit automatic operating, and monitoring management is set.
This RO concentrated solution is after this process unit is processed, and COD clearance can reach more than 91%, NH 3-N 90%,, colourity 94%, stable water outlet reaches " integrated wastewater discharge standard " emission standard (GB8978-1996).

Claims (2)

1. the equipment of a pulse electrolysis processing RO concentrated solution, comprise Fenton pretreatment pool (2), one-level settling tank (7), pulse electrolysis pond (9), second-level settling pond (15), Fenton pretreatment pool (2) is connected by pipeline (6) with one-level settling tank (7), one-level settling tank (7) connects pulse electrolysis pond (9) by transferpump (8), pulse electrolysis pond (9) connects second-level settling pond (15) by pipeline (14), it is characterized in that agitator (4) under the interior installation of Fenton pretreatment pool (2) liquid), reflux pump (5), Fenton reagent ingress pipe (3), on Fenton pretreatment pool (2), establish acid adding device (18), adder-subtractor (19), Fenton reagent device (20), positive and negative electrode (10) is housed in pulse electrolysis pond (9), electrode (10) connects the pulse power (12) and oscilloscope, agitator (13) under reflux pump (11), liquid is set, the outer electromagnetic field generator (16) of installing of second-level settling pond (15) mud-removing bucket in pulse electrolysis pond (9).
2. the equipment of RO concentrated solution is processed in a kind of pulse electrolysis as claimed in claim 1, it is characterized in that electromagnetic field generator (16) is the ring-type cone magnetic gonosome by coil winding, end portion coil is dense, and upper end portion coil is sparse, electromagnetic field generator (16) external source switch (17).
CN201420035405.4U 2014-01-21 2014-01-21 Equipment for treating RO (reverse osmosis) concentrated liquid by pulse electrolysis Withdrawn - After Issue CN203715425U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201420035405.4U CN203715425U (en) 2014-01-21 2014-01-21 Equipment for treating RO (reverse osmosis) concentrated liquid by pulse electrolysis

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201420035405.4U CN203715425U (en) 2014-01-21 2014-01-21 Equipment for treating RO (reverse osmosis) concentrated liquid by pulse electrolysis

Publications (1)

Publication Number Publication Date
CN203715425U true CN203715425U (en) 2014-07-16

Family

ID=51154593

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201420035405.4U Withdrawn - After Issue CN203715425U (en) 2014-01-21 2014-01-21 Equipment for treating RO (reverse osmosis) concentrated liquid by pulse electrolysis

Country Status (1)

Country Link
CN (1) CN203715425U (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103819029A (en) * 2014-01-21 2014-05-28 中钢集团武汉安全环保研究院有限公司 Equipment and method for treating RO (reverse osmosis) concentrate through pulse electrolysis
CN104529046A (en) * 2015-01-21 2015-04-22 中钢集团武汉安全环保研究院有限公司 Equipment and combined process for treating RO concentrated solution of high-concentration organic wastewater
CN108726740A (en) * 2018-06-11 2018-11-02 山东龙安泰环保科技有限公司 A kind of high sodium chloride waste water Zero discharge treatment method
CN113087318A (en) * 2021-05-19 2021-07-09 江苏中鹏环保集团有限公司 Advanced treatment method for landfill leachate

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103819029A (en) * 2014-01-21 2014-05-28 中钢集团武汉安全环保研究院有限公司 Equipment and method for treating RO (reverse osmosis) concentrate through pulse electrolysis
CN104529046A (en) * 2015-01-21 2015-04-22 中钢集团武汉安全环保研究院有限公司 Equipment and combined process for treating RO concentrated solution of high-concentration organic wastewater
CN108726740A (en) * 2018-06-11 2018-11-02 山东龙安泰环保科技有限公司 A kind of high sodium chloride waste water Zero discharge treatment method
CN113087318A (en) * 2021-05-19 2021-07-09 江苏中鹏环保集团有限公司 Advanced treatment method for landfill leachate

Similar Documents

Publication Publication Date Title
CN206142964U (en) Integration high concentration sewage advanced oxidation treatment equipment
CN203715425U (en) Equipment for treating RO (reverse osmosis) concentrated liquid by pulse electrolysis
CN102211830B (en) Method for treating cutting liquid wastewater by electro-catalytic oxidation
CN103145223A (en) Electrochemical reactor
CN205313291U (en) Refrigeration cycle water integrated processing system
CN101781001A (en) Method for processing effluent by two-stage electrolysis and device thereof
CN108217862B (en) Double-electrode electric flocculation-electrocatalysis ozone device and industrial wastewater treatment method
CN106830467B (en) Fenton method sewage treatment integrated device based on iron mud recycling and method thereof
CN104496008B (en) The Apparatus and method for of a kind of electrochemistry-biological coupling process organic waste water
CN104163473A (en) Novel electrochemical treatment device for wastewater treatment and wastewater treatment method
CN103819029B (en) A kind of Apparatus and method for of pulse electrolysis process RO concentrated solution
CN105384222A (en) Waste water electric flocculation treatment device
CN102887559A (en) Electrochemical reduction assistance-based biosorption integrated reactor and treatment method of hexavalent chromium-containing wastewater
CN203319806U (en) Electrolysis dephosphorization device for treating domestic sewage
CN105502754A (en) High efficiency sewage treatment method
CN209065489U (en) It is a kind of for handling the three-dimensional electrocatalysis oxidation apparatus of ammonia nitrogen waste water
CN204434420U (en) Process high concentrated organic wastewater RO concentrated solution equipment
CN104529046B (en) Process high concentrated organic wastewater RO concentrated solution equipment and group technology
CN106145460A (en) A kind of electrochemical oxidation method processes the device of dyeing waste water
CN202449955U (en) Integrated treatment device for landfill leachate
CN104445855A (en) System and method for treating breeding fecal sewage
CN205313290U (en) Cooling circulating water treatment system that can reequip on line
CN214880910U (en) Pretreatment device and process flow for zinc-containing nickel-containing electroplating wastewater
CN103936113B (en) A kind of iron charcoal reactor apparatus and treatment process processing high concentrated organic wastewater
Budiyono et al. Study on treatment of slaughterhouse wastewater by electro-coagulation technique

Legal Events

Date Code Title Description
C14 Grant of patent or utility model
GR01 Patent grant
AV01 Patent right actively abandoned

Granted publication date: 20140716

Effective date of abandoning: 20160224

C25 Abandonment of patent right or utility model to avoid double patenting