CN108218095A - The industrial wastewater treatment system of magnetic-coagulation-membrane capacitance deionization technology integration - Google Patents

The industrial wastewater treatment system of magnetic-coagulation-membrane capacitance deionization technology integration Download PDF

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Publication number
CN108218095A
CN108218095A CN201810167765.2A CN201810167765A CN108218095A CN 108218095 A CN108218095 A CN 108218095A CN 201810167765 A CN201810167765 A CN 201810167765A CN 108218095 A CN108218095 A CN 108218095A
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China
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magnetic
membrane capacitance
coagulation
capacitance deionization
deionization
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CN201810167765.2A
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Chinese (zh)
Inventor
朱亮
邓博仁
陈琳
刘畅
臧斌
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Hohai University HHU
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Hohai University HHU
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Priority to CN201810167765.2A priority Critical patent/CN108218095A/en
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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
    • C02F1/52Treatment 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
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/469Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis
    • C02F1/4691Capacitive deionisation
    • 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
    • C02F1/48Treatment of water, waste water, or sewage with magnetic or electric fields

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

Abstract

The invention discloses the industrial wastewater treatment systems of magnetic-coagulation membrane capacitance deionization technology integration, including water inlet pipe, intake pump, magnetic-coagulation system, the first peristaltic pump, membrane capacitance deionization system, magnetic-coagulation system is connected by water inlet pipe with pending wastewater disposal basin, intake pump is arranged on water inlet pipe, and through magnetic-coagulation system, treated that liquid imports membrane capacitance deionization system under the action of the first peristaltic pump.The combination that the present invention passes through magnetic-coagulation and membrane capacitance deionization, suspended matter and organic matter are attached on the anion and cation exchange membrane and electrode of capacitor deionizing instrument in effectively preventing into water, so as to ensure that the desalting processing effect of membrane capacitance deionizer, it is easy to operate and realize effectively removing for water pollutant, have that low power consuming, fouling membrane rate be low, simple operation and other advantages.

Description

The industrial wastewater treatment system of magnetic-coagulation-membrane capacitance deionization technology integration
Technical field
The invention belongs to water-treatment technology field, the more particularly to work of magnetic-coagulation-membrane capacitance deionization technology integration Industry waste water treatment system.
Background technology
Magnetic-coagulation sedimentation is the synchronous addition magnetic powder in common precipitation coagulation process, is allowed to and pollutant flocculates and ties Integrator to strengthen coagulation, flocculated effect, makes the flco density bigger, more solid of generation, so as to reach high speed settling Purpose.The residence time of entire technique is very short, therefore to most of pollutant including TP, the machine of anti-course of dissolution occurs Rate is very small, and the magnetic powder and flocculant in addition added in system has good suction to bacterium, virus, oil and a variety of fine particles Attached effect, therefore to the removal effect of the pollutant than being got well during traditional handicraft.Simultaneously because the performance of its high speed pellets, makes it Compared with traditional handicraft, have many advantages, such as that speed is fast, efficient, floor space is small.
Membrane capacitance deionization technology is a kind of efficient, low energy consumption water technology, has very high removal to imitate in ion Rate, but the anion and cation exchange membrane at membrane capacitance deionizer the two poles of the earth is easily contaminated, and film surface is blocked, cause water outlet salt Phenomena such as degree raising, effluent quality is deteriorated.Oil in Sewage Water class, colloidal substance, humate, natural organic matter, bacterium, protein etc. Easily cause amberplex seriously polluted.
Invention content
In order to solve the technical issues of above-mentioned background technology proposes, the present invention is intended to provide magnetic-coagulation-membrane capacitance deionization The industrial wastewater treatment system of technology integration, suspended matter and organic matter attach to the moon of capacitor deionizing instrument in avoiding into water On cation-exchange membrane and electrode.
In order to realize above-mentioned technical purpose, the technical scheme is that:
The industrial wastewater treatment system of a kind of magnetic-coagulation-membrane capacitance deionization technology integration, including water inlet pipe, water inlet Pump, magnetic-coagulation system, the first peristaltic pump, membrane capacitance deionization system;Magnetic-coagulation system passes through water inlet pipe and pending wastewater disposal basin Connection, intake pump are arranged on water inlet pipe;Through magnetic-coagulation system, treated that liquid imports film under the action of the first peristaltic pump Capacitive deionization system.
Further, the magnetic-coagulation system includes coagulant dosage unit, flocculant concentration unit, magnetic-coagulation reaction Pond, flocculation tank and sedimentation basin;The entrance of magnetic-coagulation reaction tank imports pending waste water, coagulant dosage list by water inlet pipe Member puts into coagulant into magnetic-coagulation reaction tank and is reacted, and the liquid after reaction is imported flocculation tank, and flocculant is thrown Unit is added to be reacted, and the liquid after reaction is imported sedimentation basin to flocculation tank input flocculant, is further sunk It forms sediment, the supernatant liquor of sedimentation basin imports membrane capacitance deionization system under the action of the first peristaltic pump.
Further, the magnetic-coagulation system further includes return sludge pump, magnetic powder recovering device, magnetic powder and adds unit, remains Remaining sludge pump and sludge pipe, the sludge under sedimentation basin precipitates import magnetic powder recovering device under returned sludge pumping action, detach To recycling magnetic powder and excess sludge, the recycling magnetic powder adds unit by magnetic powder and puts into again in magnetic-coagulation reaction tank, and remains Remaining sludge passes through sludge pipe discharge system under the action of residual sludge pump.
Further, the membrane capacitance deionization system includes clean solution tank, the second peristaltic pump, third peristaltic pump, the first film Capacitive deionization component, the second membrane capacitance deionization, water outlet pump, conductivity measuring instrument and tank;Through magnetic-coagulation system Treated, and liquid is imported in clean solution tank, and under the action of the second peristaltic pump, the liquid in clean solution tank imports the first membrane capacitance and goes Salinity removal is carried out in deionization unit, through the first membrane capacitance deionization treated liquid again in the effect of third peristaltic pump Under, it imports in the second membrane capacitance deionization and carries out secondary salinity removal, treated through the second membrane capacitance deionization Liquid is imported under the action of water outlet pump in tank, the conductivity of liquid in conductivity measuring instrument detection tank.
Further, the first membrane capacitance deionization and the second membrane capacitance deionization use direct current constant current control Molding formula is 0.2-3.5mA/cm in current density2Lower operation.
Further, the membrane capacitance deionization system further includes regeneration flow container, and memory contains flushing water;When in tank When the conductivity of liquid rises or membrane capacitance deionization both end voltage is more than 1.2V, electrode adsorption ion reaches saturation, Into regeneration stage, membrane capacitance is rinsed by membrane capacitance deionization two-plate reversal connection, and to regenerate the flushing water in flow container The two-plate of deionization unit realizes ion desorption, this process uses direct current constant voltage control model, that is, controls membrane capacitance deionization Component both end voltage carries out the regeneration of electrode for 1.2V, and regenerative process carries out to flushing water water outlet conductivity no longer changing, Regeneration stage terminates.
Further, the first membrane capacitance deionization and the second membrane capacitance deionization are loaded using graphite flake Active carbon fiber felt, be furnished with anions and canons exchange membrane on active carbon fiber felt surface.
The advantageous effect brought using above-mentioned technical proposal:
The present invention adds magnetic-coagulation device before membrane capacitance deionizer, forms group technology, is precipitated using magnetic-coagulation The pollutants such as organic matter avoid Organic substance in water from being adsorbed on amberplex or electrode to reach, and improve membrane capacitance deionization The desalting efficiency of component considerably increases the service life of device, so as to ensure the treatment effect of membrane capacitance deionization.
Description of the drawings
Fig. 1 is the system composition schematic diagram of the present invention.
Specific embodiment
Below with reference to attached drawing, technical scheme of the present invention is described in detail.
A kind of industrial wastewater treatment system of magnetic-coagulation-membrane capacitance deionization technology integration, as shown in Figure 1, including into Water pipe 1, intake pump 2, magnetic-coagulation system, the first peristaltic pump 13, membrane capacitance deionization system;Magnetic-coagulation system passes through water inlet pipe 1 It is connected with pending wastewater disposal basin, intake pump 2 is arranged on water inlet pipe 1;It wriggles through magnetic-coagulation system treated liquid first Membrane capacitance deionization system is imported under the action of pump 13.
Magnetic-coagulation system includes coagulant dosage unit 3, flocculant concentration unit 4, magnetic-coagulation reaction tank 5, flocculation reaction Pond 6 and sedimentation basin 7;The entrance of magnetic-coagulation reaction tank 5 imports pending waste water by water inlet pipe 1, and coagulant dosage unit 3 is to magnetic Coagulant is put into coagulation reaction tank 5 to be reacted, and the liquid after reaction is imported flocculation tank 6, flocculant concentration list Member 4 puts into flocculant to flocculation tank 6 and is reacted, and the liquid after reaction is imported sedimentation basin 7, is further sunk It forms sediment, the supernatant liquor of sedimentation basin 7 imports membrane capacitance deionization system under the action of the first peristaltic pump 13.
Magnetic-coagulation system further includes return sludge pump 8, magnetic powder recovering device 9, magnetic powder and adds unit 10, residual sludge pump 11 With sludge pipe 12, the lower sludge of the precipitation of sedimentation basin 7 importing magnetic powder recovering device 9 under the effect of return sludge pump 8, isolated time Magnetic powder and excess sludge are received, the recycling magnetic powder adds unit 10 by magnetic powder and puts into magnetic-coagulation reaction tank 5 again, and remaining Sludge passes through 12 discharge system of sludge pipe under the action of residual sludge pump 11.Magnetic powder recovering device 9 includes interconnected height Fast cutter and magnetic separator, the sludge first enter back into magnetic separator after high-speed shearing machine is sheared, are detached through magnetic separator Processing is recycled magnetic powder and excess sludge.
Membrane capacitance deionization system includes clean solution tank, the second peristaltic pump 14, third peristaltic pump 15, the first membrane capacitance deionization Component 16, the second membrane capacitance deionization 17, water outlet pump 19, conductivity measuring instrument 20 and tank 21;Through magnetic-coagulation system Treated, and liquid is imported in clean solution tank, and under the action of the second peristaltic pump 14, the liquid in clean solution tank imports the first membrane capacitance Salinity removal is carried out in deionization 16, through the first membrane capacitance deionization 16 treated liquid again in third peristaltic pump Under the action of 15, import in the second membrane capacitance deionization 17 and carry out secondary salinity removal, through the second membrane capacitance deionization group Treated the liquid of part 17 is imported under the action of water outlet pump 19 in tank 21, and conductivity measuring instrument 20 is detected in tank 21 The conductivity of liquid.
First membrane capacitance deionization 16 and the second membrane capacitance deionization 17 use direct current constant current controlling mould Formula is 0.2-3.5mA/cm in current density2Lower operation.Membrane capacitance deionization I realizes the salinity removal of 60%-75%, Membrane capacitance deionization II realizes the salinity removal of 90%-95% in I water outlet of membrane capacitance deionization.
Membrane capacitance deionization system further includes regeneration flow container 18, and memory contains flushing water;When the electricity of liquid in tank 21 When conductance rises or membrane capacitance deionization both end voltage is more than 1.2V, electrode adsorption ion reaches saturation, into regeneration Stage, by membrane capacitance deionization two-plate reversal connection, and to regenerate the raw water flushing membrane capacitive deionization component in flow container 18 Two-plate, realize ion desorption, this process uses direct current constant voltage control model, that is, controls membrane capacitance deionization both ends Voltage carries out the regeneration of electrode for 1.2V, and regenerative process carries out to flushing water water outlet conductivity no longer changing, regeneration stage Terminate.After the first use of flushing water in storage to regeneration flow container 18, continue on for the next regeneration period, recycled.
In the present embodiment, water inlet sewage quality parameter is:TOC be 6-8mg/L, main organic components be grease, nothing Machine object ingredient be sodium chloride, conductivity 13-14mS/cm, 20 DEG C of water temperature.So set, simulate typical sanitary sewage Water quality.
Membrane capacitance deionization contains 100 groups of electrodes, and membrane capacitance device is the active carbon fiber felt of graphite flake load, It is 10 × 10cm per plate electrode area2, graphite flake is collector, and anions and canons exchange membrane is furnished on active carbon fiber felt surface, First membrane capacitance deionization and the second membrane capacitance deionization are using direct current constant current controlling pattern, the first film electricity It is 0.6mA/cm to hold deionization in current density2Lower operation, 8 minutes, water outlet conductivity 3-4mS/cm residence time, the Two membrane capacitance deionizations are 0.25mA/cm in current density2Lower operation, 10 minutes residence times, water outlet conductivity is less than 0.5mS/cm。
In common deionization technology, such as ion-exchange, electroosmose process, hyperfiltration.There is very for these methods More limitations, such as using hyperfiltration, system is very high to the pre-processing requirements of water, and water producing cost is high;Using ion-exchange, then Raw soda acid is costly, and regeneration liquid waste is easy to cause environment secondary pollution, and systems operational requirement is high;Using electroosmose process, fortune Easy fouling on cathode and anode film during row, so as to influence effluent quality.And membrane capacitance deionization technology have low energy consumption, The advantages such as membrane fouling rate is low.
Oil in Sewage Water class, colloidal substance, humate, natural organic matter, bacterium, protein etc. easily cause amberplex It is seriously polluted.The anion and cation exchange membrane at membrane capacitance deionizer the two poles of the earth is easily contaminated, and film surface blocks, and influences membrane capacitance and goes The desalting efficiency of deionization unit.Organic matter etc. easily attaches to ion exchange film surface, can not only greatly shorten the use of device Service life, but also can increase regenerated difficulty.Present invention process adds magnetic-coagulation sedimentation basin before membrane capacitance deionization, Group technology is formed, using pollutants such as magnetic-coagulation precipitating organic matters, Organic substance in water is avoided to be adsorbed in ion exchange to reach On film or electrode, so as to ensure the purpose of membrane capacitance deionization treatment effect.
Embodiment is merely illustrative of the invention's technical idea, it is impossible to protection scope of the present invention is limited with this, it is every according to Technological thought proposed by the present invention, any change done on the basis of technical solution, each falls within the scope of the present invention.

Claims (7)

1. a kind of industrial wastewater treatment system of magnetic-coagulation-membrane capacitance deionization technology integration, it is characterised in that:Including water inlet Manage (1), intake pump (2), magnetic-coagulation system, the first peristaltic pump (13), membrane capacitance deionization system;Magnetic-coagulation system passes through water inlet Pipe (1) is connected with pending wastewater disposal basin, and intake pump (2) is arranged on water inlet pipe (1);Through magnetic-coagulation system, treated that liquid exists Membrane capacitance deionization system is imported under the action of first peristaltic pump (13).
2. the industrial wastewater treatment system of magnetic-coagulation-membrane capacitance deionization technology integration according to claim 1, feature It is:The magnetic-coagulation system includes coagulant dosage unit (3), flocculant concentration unit (4), magnetic-coagulation reaction tank (5), wadding Solidifying reaction tank (6) and sedimentation basin (7);The entrance of magnetic-coagulation reaction tank (5) imports pending waste water, coagulation by water inlet pipe (1) Agent adds unit (3) input coagulant into magnetic-coagulation reaction tank (5) and is reacted, and the liquid after reaction is imported flocculation instead Ying Chi (6), flocculant concentration unit (4) are reacted, and the liquid after reaction is led to flocculation tank (6) input flocculant Enter sedimentation basin (7), further precipitated, the supernatant liquor of sedimentation basin (7) imports film under the action of the first peristaltic pump (13) Capacitive deionization system.
3. the industrial wastewater treatment system of magnetic-coagulation-membrane capacitance deionization technology integration according to claim 2, feature It is:The magnetic-coagulation system further includes return sludge pump (8), magnetic powder recovering device (9), magnetic powder and adds unit (10), residue Sludge pump (11) and sludge pipe (12), the sludge under sedimentation basin (7) precipitates import magnetic powder recycling under return sludge pump (8) effect Device (9), isolated recycling magnetic powder and excess sludge, the recycling magnetic powder add unit (10) by magnetic powder and put into magnetic again In coagulation reaction tank (5), and excess sludge passes through sludge pipe (12) discharge system under the action of residual sludge pump (11).
4. the industrial wastewater treatment system of magnetic-coagulation-membrane capacitance deionization technology integration according to claim 1, feature It is:The membrane capacitance deionization system includes clean solution tank, the second peristaltic pump (14), third peristaltic pump (15), the first membrane capacitance Deionization (16), the second membrane capacitance deionization (17), water outlet pump (19), conductivity measuring instrument (20) and tank (21);It is imported in clean solution tank through magnetic-coagulation system treated liquid, under the action of the second peristaltic pump (14), in clean solution tank Liquid, which imports, carries out salinity removal in the first membrane capacitance deionization (16), handled through the first membrane capacitance deionization (16) Liquid afterwards under the action of third peristaltic pump (15), imports and secondary salinity is carried out in the second membrane capacitance deionization (17) again Removal, through the second membrane capacitance deionization (17), treated that liquid imports tank (21) under the action of water outlet pump (19) In, the conductivity of liquid in conductivity measuring instrument (20) detection tank (21).
5. the industrial wastewater treatment system of magnetic-coagulation-membrane capacitance deionization technology integration according to claim 4, feature It is:First membrane capacitance deionization (16) and the second membrane capacitance deionization (17) use direct current constant current controlling mould Formula is 0.2-3.5mA/cm in current density2Lower operation.
6. the industrial wastewater treatment system of magnetic-coagulation-membrane capacitance deionization technology integration according to claim 5, feature It is:The membrane capacitance deionization system further includes regeneration flow container (18), and memory contains flushing water;When liquid in tank (21) Conductivity rise or membrane capacitance deionization both end voltage be more than 1.2V when, electrode adsorption ion reaches saturation, enter Regeneration stage, by membrane capacitance deionization two-plate reversal connection, and with regenerate the raw water in flow container (18) rinse membrane capacitance go from The two-plate of sub-component realizes ion desorption, this process uses direct current constant voltage control model, that is, controls membrane capacitance deionization group Part both end voltage carries out the regeneration of electrode for 1.2V, and regenerative process carries out to flushing water water outlet conductivity no longer changing, then The raw stage terminates.
7. the industrial wastewater treatment system of magnetic-coagulation-membrane capacitance deionization technology integration according to claim 4, feature It is:The work that the first membrane capacitance deionization (16) and the second membrane capacitance deionization (17) are loaded using graphite flake Property Carbon fibe felt, anions and canons exchange membrane is furnished on active carbon fiber felt surface.
CN201810167765.2A 2018-02-28 2018-02-28 The industrial wastewater treatment system of magnetic-coagulation-membrane capacitance deionization technology integration Pending CN108218095A (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109593956A (en) * 2018-12-10 2019-04-09 核工业北京化工冶金研究院 A kind of enriching apparatus and method of uranium solution
CN110526354A (en) * 2019-08-27 2019-12-03 首创爱华(天津)市政环境工程有限公司 A method of utilizing magnetic-coagulation technical treatment industrial wastewater

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US20080073268A1 (en) * 2006-09-27 2008-03-27 Cort Steven L Use of a magnetic separator to biologically clean water
CN102992533A (en) * 2011-09-16 2013-03-27 常熟科勒有限公司 Paint wastewater treatment system
CN103819045A (en) * 2014-01-26 2014-05-28 浙江省环境保护科学设计研究院 Wastewater reuse method combining magnetic loading coagulation clarification and membrane separation
CN205088054U (en) * 2015-07-30 2016-03-16 坎布里奇环保科技(北京)有限公司 Integration magnetism thoughtlessly congeals water treatment facilities
CN106745552A (en) * 2016-12-08 2017-05-31 河海大学 Membrane capacitance deionizer and its application using composite photocatalyst fiber filter
CN106865837A (en) * 2017-03-01 2017-06-20 河海大学 A kind of method of utilization milipore filter and membrane capacitance deionization group technology treatment brackish-water lake storehouse water

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20080073268A1 (en) * 2006-09-27 2008-03-27 Cort Steven L Use of a magnetic separator to biologically clean water
CN102992533A (en) * 2011-09-16 2013-03-27 常熟科勒有限公司 Paint wastewater treatment system
CN103819045A (en) * 2014-01-26 2014-05-28 浙江省环境保护科学设计研究院 Wastewater reuse method combining magnetic loading coagulation clarification and membrane separation
CN205088054U (en) * 2015-07-30 2016-03-16 坎布里奇环保科技(北京)有限公司 Integration magnetism thoughtlessly congeals water treatment facilities
CN106745552A (en) * 2016-12-08 2017-05-31 河海大学 Membrane capacitance deionizer and its application using composite photocatalyst fiber filter
CN106865837A (en) * 2017-03-01 2017-06-20 河海大学 A kind of method of utilization milipore filter and membrane capacitance deionization group technology treatment brackish-water lake storehouse water

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109593956A (en) * 2018-12-10 2019-04-09 核工业北京化工冶金研究院 A kind of enriching apparatus and method of uranium solution
CN109593956B (en) * 2018-12-10 2020-08-21 核工业北京化工冶金研究院 Uranium solution enrichment device and method
CN110526354A (en) * 2019-08-27 2019-12-03 首创爱华(天津)市政环境工程有限公司 A method of utilizing magnetic-coagulation technical treatment industrial wastewater

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