CN106495379A - A kind of electroplating rinse water circulating and recovering and heavy metal recovery technique - Google Patents

A kind of electroplating rinse water circulating and recovering and heavy metal recovery technique Download PDF

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Publication number
CN106495379A
CN106495379A CN201611064717.8A CN201611064717A CN106495379A CN 106495379 A CN106495379 A CN 106495379A CN 201611064717 A CN201611064717 A CN 201611064717A CN 106495379 A CN106495379 A CN 106495379A
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reverse osmosis
rinse water
membrane
heavy metal
water
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CN106495379B (en
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杜建伟
贺框
项赟
张明杨
石海佳
温勇
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South China Institute of Environmental Science of Ministry of Ecology and Environment
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South China Institute of Environmental Science of Ministry of Ecology and Environment
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    • 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
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • 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
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • C02F1/32Treatment of water, waste water, or sewage by irradiation with ultraviolet light
    • 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
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/441Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by reverse osmosis
    • 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
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/442Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by nanofiltration
    • 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
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/444Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by ultrafiltration or microfiltration
    • 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
    • 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
    • C02F2101/20Heavy metals or heavy metal compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/16Nature of the water, waste water, sewage or sludge to be treated from metallurgical processes, i.e. from the production, refining or treatment of metals, e.g. galvanic wastes
    • 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
    • C02F2209/04Oxidation reduction potential [ORP]
    • 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
    • C02F2209/06Controlling or monitoring parameters in water treatment pH
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/08Multistage treatments, e.g. repetition of the same process step under different conditions

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  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

The invention discloses a kind of electroplating rinse water circulating and recovering and heavy metal recovery technique:By rinse bath discharge electroplating rinse water filters → further concentrate through milipore filter ultrafiltration → entrances nanofiltration membrane treatment → entrances first-stage reverse osmosis membranous system through security filtration system, milipore filter, NF membrane, first-stage reverse osmosis film produce water enter two-pass reverse osmosis film process → two-pass reverse osmosis film concentrated water return first-stage reverse osmosis membranous system concentration → using efficient photoelectricity treater catalytic unit to concentration after electroplating rinse water carry out process recovery heavy metal.The present invention is using membrane technology and photo-electrocatalytic technology, it is achieved that the circulating and recovering of electroplating rinse water, reduces plating industrial water amount, while the heavy metal resources in online recycling washings.The technology can reduce electroplating cleaning water consumption to greatest extent, while reducing pollution of the electroplating rinse water to environment.

Description

A kind of electroplating rinse water circulating and recovering and heavy metal recovery technique
Technical field
The present invention relates to Industrial Wastewater Treatment and utilization technology field, are specifically related to a kind of electroplate rinsing water circulation Reuse and heavy metal recovery technique.
Background technology
Plating is in order to improve the physical and chemical performances such as the electric conductivity of material, wearability, corrosion resistance, using electrochemistry original Reason, in the process that metal or non-metal material surface plate layer of metal or alloy.After plating terminates, need to plating piece table Face carries out thoroughly cleaning, therefore has substantial amounts of electroplate rinsing wastewater and produces, and electroplate rinsing water consumption accounts for electroplating industry total water More than the 80% of amount.
Electroplate the part as processing and manufacturing, it has also become the ring that its people Ministry of Industry of China can or lack.But electroplate simultaneously During often have substantial amounts of poaching wastewater to produce, typically contain substantial amounts of heavy metal ion, buffer salt, network in these waste water Ecological environmental and human health impacts, if being unable to effective process, can be caused serious harm by the materials such as mixture.
At present, the main methods of electroplating wastewater have chemical precipitation method, absorption method, micro-electrolysis method, ion-exchange etc., These methods generally require to add substantial amounts of sewage treatment drug, high cost;It is difficult to the huge sum of money for removing complex state in electroplating wastewater Category, produces shipwreck to be up to state standards;The circulating and recovering of electroplating rinse water cannot be realized, while the heavy metal recovery in washings Difficulty, causes the wasting of resources;Substantial amounts of sludge is produced, secondary pollution is easily caused.
At present, the method for reclaiming heavy metal from electroplating wastewater is most for first adding chemical agent in electroplating wastewater, will Heavy metal precipitation in waste water is separated, then reclaims precious metal from sludge, and this method technological process is long, and consumes substantial amounts of Medicament.
Content of the invention
Big for electroplating rinse water yield, the present situation of difficult treatment, the present invention is intended to provide a kind of electroplate rinsing water circulation Reuse and the new technology of heavy metal online recycling, can both reduce the water consumption of electroplate rinsing process, can fully reclaim weight again Metals resources, eliminate pollution on the environment.
The technical scheme is that:A kind of electroplating rinse water circulating and recovering and heavy metal recovery technique, including following step Suddenly:
1) through security filtration system, it is 0.5~5 μm to select pore size filter to the electroplating rinse water for discharging rinse bath, goes Except the granule foreign in waste water;
2) by the electroplating rinse water filtered through security filter through milipore filter, selection pore size filter is 0.005~0.01 μ The hollow fiber ultrafiltration membrane of m, removes the macromolecular organic pollution in washings, while washings are carried out with initial concentration, passes through The concentration of electroplating rinse water can be lifted 2 to 3 times by milipore filter;
3) concentrated water of the electroplating rinse water after milipore filter initial concentration enters nanofiltration membrane treatment system and further processes, Nanofiltration membrane aperture is 1-2nm, and NF membrane can retain the most organic matters in rinse water and more than 80% divalent ion, Simultaneously being separated by filtration by NF membrane, can be by more than 10 times again of the concentration of electroplating rinse water;
4) concentrated water through nanofiltration membrane treatment enters first-stage reverse osmosis membranous system and further concentrates, by the dense of electroplating rinse water Degree lifts 5-100 times, makes the concentration of heavy metal ion of product water less than 1mg/L, and electrical conductivity reaches water for cleaning less than 50us/cm Standard, can be with direct circulation reuse;Almost all of ionic species can be retained in rinse water using first-stage reverse osmosis film and had Machine material;
5) milipore filter, NF membrane, the product water of first-stage reverse osmosis film enter two-pass reverse osmosis film, at two-pass reverse osmosis film Reason, makes the concentration of heavy metal ion of product water be reduced to below 1mg/L, and electrical conductivity is fully achieved water for cleaning mark less than 50us/cm Standard, used as washings direct reuse;
6) concentrated water of two-pass reverse osmosis film returns first-stage reverse osmosis membranous system concentration;
7) using efficient photoelectricity treater catalytic unit to concentration after electroplating rinse water process, by electroplating rinse water pH value adjust Save as 4-9, the organic matter in electroplating rinse water is deposited in cathodic reduction in titanium dioxide anodic oxidation, heavy metal, the negative electrode Current potential is Ec=-0.9V -1.5V, and anode potential is 2-10V.Through photoelectro catalytic system, the COD concentration in washings is dropped As little as below 60mg/L, concentration of heavy metal ion are fully achieved electroplating wastewater discharge standard less than 0.1mg/L.
Further, in such scheme, electroplating rinse water first passes through classification before the security filtration system Collect, be easy to reclaim highly purified single heavy metal.
Further, in such scheme, step 7) described in efficient photoelectricity treater catalytic unit be photoelectricity from titanium dioxide Pole.
Further, in such scheme, step 7) described in efficient photoelectricity treater catalytic unit be light source from ultraviolet light, electricity Current density is 0.5-1.5mA/cm2.
Further, in such scheme, step 3) membrane module of the NF membrane is rolled membrane module or tubular membrane group Part, its condition of work are 15~40 DEG C, and operating pressure is 4~10bar.
Further, in such scheme, the first-stage reverse osmosis film is polyamide reverse osmose membrane.
Further, in such scheme, the two-pass reverse osmosis film is nanometer silicon carbide complex reverse osmosis membrane;Described receive Rice silicon carbide compound reverse osmosis membrane preparation method be:Nanometer silicon carbide particle is pressed (0.001-0.01):(3-10) weight Than being added in nitric acid ethyl ammonium salt solution, the nanometer silicon carbide even particulate dispersion is made in nitric acid diethyl ammonium solution, then Porous support membrane is immersed in solution, is heat-treated, that is, obtain nanometer silicon carbide complex reverse osmosis membrane.The open support Film is PS membrane, and the temperature of the heat treatment is 50-80 DEG C, and the duration of the heat treatment is 10-20 minutes.
The invention has the beneficial effects as follows:The present invention is using membrane technology and photo-electrocatalytic technology, it is achieved that electroplate rinsing The circulating and recovering of water, reduces plating industrial water amount, while the heavy metal resources in online recycling washings.The technology can be with Electroplating cleaning water consumption is reduced to greatest extent, while reducing pollution of the electroplating rinse water to environment.
Description of the drawings
Fig. 1 is the process chart of the present invention.
Specific embodiment
The present invention is further described in detail with reference to specific embodiment:
Embodiment 1
A kind of electroplating rinse water circulating and recovering and heavy metal recovery technique, comprise the following steps:
1) electroplating rinse water that rinse bath is discharged is first passed through categorised collection, is easy to reclaim highly purified single heavy metal, Then through security filtration system, it is 0.5 μm to select pore size filter, removes the granule foreign in waste water;
2) by the electroplating rinse water filtered through security filter through milipore filter, it is in 0.005 μm to select pore size filter Fibre ultrafiltration film, removes the macromolecular organic pollution in washings, while initial concentration is carried out to washings, through ultrafiltration The concentration of electroplating rinse water can be lifted 2 times by film;
3) concentrated water of the electroplating rinse water after milipore filter initial concentration enters nanofiltration membrane treatment system and further processes, Nanofiltration membrane aperture is 1nm, and the membrane module of NF membrane is rolled membrane module or tubular membrane component, and its condition of work is 15 DEG C, work Pressure is 4bar;NF membrane can retain the most organic matters in rinse water and more than 80% divalent ion, while logical Being separated by filtration for NF membrane is crossed, can be by more than 10 times again of the concentration of electroplating rinse water;
4) concentrated water through nanofiltration membrane treatment enters first-stage reverse osmosis membranous system and further concentrates, and first-stage reverse osmosis film is poly- The concentration of electroplating rinse water is lifted 5 times by acid amides reverse osmosis membrane, makes the concentration of heavy metal ion of product water less than 1mg/L, electrical conductivity Less than 50us/cm, water for cleaning standard is reached, can be with direct circulation reuse;Rinse water can be retained using first-stage reverse osmosis film In almost all of ionic species and organic substance;
5) milipore filter, NF membrane, the product water of first-stage reverse osmosis film enter two-pass reverse osmosis film, at two-pass reverse osmosis film Reason, makes the concentration of heavy metal ion of product water be reduced to below 1mg/L, and electrical conductivity is fully achieved water for cleaning mark less than 50us/cm Standard, used as washings direct reuse;Two-pass reverse osmosis film is nanometer silicon carbide complex reverse osmosis membrane;Nanometer silicon carbide is combined reverse osmosis The preparation method of permeable membrane is:Nanometer silicon carbide particle is pressed 0.001:3 weight ratio is added in nitric acid ethyl ammonium salt solution, makes institute Nanometer silicon carbide even particulate dispersion is stated in nitric acid diethyl ammonium solution, then porous support membrane is immersed in solution, carried out Heat treatment, porous support membrane are PS membrane, and the temperature of heat treatment is 50 DEG C, and the duration of heat treatment is 10 minutes;Obtain Nanometer silicon carbide complex reverse osmosis membrane;
6) concentrated water of two-pass reverse osmosis film returns first-stage reverse osmosis membranous system concentration;
7) using efficient photoelectricity treater catalytic unit to concentration after electroplating rinse water process, from titanium dioxide be photoelectricity Pole, is light source from ultraviolet light, and current density is 0.5mA/cm2;Electroplating rinse water pH value is adjusted to 4, in electroplating rinse water Organic matter in titanium dioxide anodic oxidation, heavy metal is deposited in cathodic reduction, and the cathode potential is Ec=-0.9V, anode Current potential is 2V;Through photoelectro catalytic system, the COD concentration in washings is reduced to below 60mg/L, concentration of heavy metal ion Less than 0.1mg/L, electroplating wastewater discharge standard is fully achieved.
Embodiment 2
A kind of electroplating rinse water circulating and recovering and heavy metal recovery technique, comprise the following steps:
1) electroplating rinse water that rinse bath is discharged is first passed through categorised collection, is easy to reclaim highly purified single heavy metal, Then through security filtration system, it is 2.75 μm to select pore size filter, removes the granule foreign in waste water;
2) by the electroplating rinse water filtered through security filter through milipore filter, it is in 0.0075 μm to select pore size filter Fibre ultrafiltration film, removes the macromolecular organic pollution in washings, while initial concentration is carried out to washings, through ultrafiltration The concentration of electroplating rinse water can be lifted 2.5 times by film;
3) concentrated water of the electroplating rinse water after milipore filter initial concentration enters nanofiltration membrane treatment system and further processes, Nanofiltration membrane aperture is 1.5nm, and the membrane module of NF membrane is rolled membrane module or tubular membrane component, and its condition of work is 27.5 DEG C, Operating pressure is 7bar;NF membrane can retain the most organic matters in rinse water and more than 80% divalent ion, with When being separated by filtration by NF membrane, can be by the concentration of electroplating rinse water again more than 10 times;
4) concentrated water through nanofiltration membrane treatment enters first-stage reverse osmosis membranous system and further concentrates, and first-stage reverse osmosis film is poly- The concentration of electroplating rinse water is lifted 52 times by acid amides reverse osmosis membrane, makes the concentration of heavy metal ion of product water less than 1mg/L, conductance Rate reaches water for cleaning standard less than 50us/cm, can be with direct circulation reuse;Cleaning can be retained using first-stage reverse osmosis film Almost all of ionic species and organic substance in water;
5) milipore filter, NF membrane, the product water of first-stage reverse osmosis film enter two-pass reverse osmosis film, at two-pass reverse osmosis film Reason, makes the concentration of heavy metal ion of product water be reduced to below 1mg/L, and electrical conductivity is fully achieved water for cleaning mark less than 50us/cm Standard, used as washings direct reuse;Two-pass reverse osmosis film is nanometer silicon carbide complex reverse osmosis membrane;Nanometer silicon carbide is combined reverse osmosis The preparation method of permeable membrane is:Nanometer silicon carbide particle is pressed 0.0055:6.5 weight ratio is added in nitric acid ethyl ammonium salt solution, The nanometer silicon carbide even particulate dispersion is made in nitric acid diethyl ammonium solution, then porous support membrane is immersed in solution, It is heat-treated, porous support membrane is PS membrane, and the temperature of heat treatment is 65 DEG C, and the duration of heat treatment is 15 minutes;I.e. Obtain nanometer silicon carbide complex reverse osmosis membrane;
6) concentrated water of two-pass reverse osmosis film returns first-stage reverse osmosis membranous system concentration;
7) using efficient photoelectricity treater catalytic unit to concentration after electroplating rinse water process, from titanium dioxide be photoelectricity Pole, is light source from ultraviolet light, and current density is 1.0mA/cm2;Electroplating rinse water pH value is adjusted to 6.5, electroplating rinse water In organic matter in titanium dioxide anodic oxidation, heavy metal is deposited in cathodic reduction, and the cathode potential is Ec=-1.2V, sun Electrode potential is 6V;Through photoelectro catalytic system, the COD concentration in washings is reduced to below 60mg/L, heavy metal ion is dense Degree is fully achieved electroplating wastewater discharge standard less than 0.1mg/L.
Embodiment 3
A kind of electroplating rinse water circulating and recovering and heavy metal recovery technique, comprise the following steps:
1) electroplating rinse water that rinse bath is discharged is first passed through categorised collection, is easy to reclaim highly purified single heavy metal, Then through security filtration system, it is 5 μm to select pore size filter, removes the granule foreign in waste water;
2) by the electroplating rinse water filtered through security filter through milipore filter, it is 0.01 μm hollow to select pore size filter Fiber ultrafiltration membrane, removes the macromolecular organic pollution in washings, while initial concentration is carried out to washings, through milipore filter, The concentration of electroplating rinse water can be lifted 3 times;
3) concentrated water of the electroplating rinse water after milipore filter initial concentration enters nanofiltration membrane treatment system and further processes, Nanofiltration membrane aperture is 2nm, and the membrane module of NF membrane is rolled membrane module or tubular membrane component, and its condition of work is 40 DEG C, work Pressure is 10bar;NF membrane can retain the most organic matters in rinse water and more than 80% divalent ion, while logical Being separated by filtration for NF membrane is crossed, can be by more than 10 times again of the concentration of electroplating rinse water;
4) concentrated water through nanofiltration membrane treatment enters first-stage reverse osmosis membranous system and further concentrates, and first-stage reverse osmosis film is poly- The concentration of electroplating rinse water is lifted 100 times by acid amides reverse osmosis membrane, makes the concentration of heavy metal ion of product water less than 1mg/L, conductance Rate reaches water for cleaning standard less than 50us/cm, can be with direct circulation reuse;Cleaning can be retained using first-stage reverse osmosis film Almost all of ionic species and organic substance in water;
5) milipore filter, NF membrane, the product water of first-stage reverse osmosis film enter two-pass reverse osmosis film, at two-pass reverse osmosis film Reason, makes the concentration of heavy metal ion of product water be reduced to below 1mg/L, and electrical conductivity is fully achieved water for cleaning mark less than 50us/cm Standard, used as washings direct reuse;Two-pass reverse osmosis film is nanometer silicon carbide complex reverse osmosis membrane;Nanometer silicon carbide is combined reverse osmosis The preparation method of permeable membrane is:Nanometer silicon carbide particle is pressed 0.01:10 weight ratio is added in nitric acid ethyl ammonium salt solution, makes institute Nanometer silicon carbide even particulate dispersion is stated in nitric acid diethyl ammonium solution, then porous support membrane is immersed in solution, carried out Heat treatment, porous support membrane are PS membrane, and the temperature of heat treatment is 80 DEG C, and the duration of heat treatment is 20 minutes;Obtain Nanometer silicon carbide complex reverse osmosis membrane;
6) concentrated water of two-pass reverse osmosis film returns first-stage reverse osmosis membranous system concentration;
7) using efficient photoelectricity treater catalytic unit to concentration after electroplating rinse water process, from titanium dioxide be photoelectricity Pole, is light source from ultraviolet light, and current density is 1.5mA/cm2;Electroplating rinse water pH value is adjusted to 9, in electroplating rinse water Organic matter in titanium dioxide anodic oxidation, heavy metal is deposited in cathodic reduction, and the cathode potential is Ec=-1.5V, anode Current potential is 10V;Through photoelectro catalytic system, the COD concentration in washings is reduced to below 60mg/L, concentration of heavy metal ion Less than 0.1mg/L, electroplating wastewater discharge standard is fully achieved.
With the above-mentioned desirable embodiment according to the present invention as enlightenment, by above-mentioned description, relevant staff is complete Various change and modification can be carried out entirely in the range of without departing from this invention technological thought.The technology of this invention Property scope is not limited to the content on specification, it is necessary to determine its technical scope according to right.

Claims (7)

1. a kind of electroplating rinse water circulating and recovering and heavy metal recovery technique, it is characterised in that comprise the following steps:
1) through security filtration system, it is 0.5~5 μm to select pore size filter to the electroplating rinse water for discharging rinse bath, removes useless Granule foreign in water;
2) by the electroplating rinse water filtered through security filter through milipore filter, selection pore size filter is 0.005~0.01 μm of left side Right hollow fiber ultrafiltration membrane, removes the macromolecular organic pollution in washings, while carrying out initial concentration to washings;
3) concentrated water of the electroplating rinse water after milipore filter initial concentration enters nanofiltration membrane treatment system and further processes, nanofiltration Membrane aperture is 1-2nm;
4) concentrated water through nanofiltration membrane treatment enters first-stage reverse osmosis membranous system and further concentrates, and the concentration of electroplating rinse water is carried About 5-100 times is risen, makes the concentration of heavy metal ion of product water less than 1mg/L, electrical conductivity reaches water for cleaning mark less than 50us/cm Standard, can be with direct circulation reuse;
5) milipore filter, NF membrane, the product water of first-stage reverse osmosis film enter two-pass reverse osmosis film, through two-pass reverse osmosis film process, The concentration of heavy metal ion of product water is made to be reduced to below 1mg/L, electrical conductivity is fully achieved water for cleaning standard less than 50us/cm, As washings direct reuse;
6) concentrated water of two-pass reverse osmosis film returns first-stage reverse osmosis membranous system concentration;
7) using efficient photoelectricity treater catalytic unit to concentration after electroplating rinse water process, electroplating rinse water pH value is adjusted to 4-9, the organic matter in electroplating rinse water are deposited in cathodic reduction in titanium dioxide anodic oxidation, heavy metal.
2. a kind of electroplating rinse water circulating and recovering according to claim 1 and heavy metal recovery technique, it is characterised in that electricity Plating washings first pass through categorised collection, are easy to reclaim highly purified single heavy metal before the security filtration system.
3. a kind of electroplating rinse water circulating and recovering according to claim 1 and heavy metal recovery technique, it is characterised in that step Rapid 7) described in efficient photoelectricity treater catalytic unit from titanium dioxide be optoelectronic pole.
4. a kind of electroplating rinse water circulating and recovering according to claim 1 and heavy metal recovery technique, it is characterised in that step Rapid 7) described in efficient photoelectricity treater catalytic unit from ultraviolet light be light source.
5. a kind of electroplating rinse water circulating and recovering according to claim 1 and heavy metal recovery technique, it is characterised in that step The membrane module of rapid 3) described NF membrane is rolled membrane module or tubular membrane component, and its condition of work is 15~40 DEG C, operating pressure For 4~10bar.
6. a kind of electroplating rinse water circulating and recovering according to claim 1 and heavy metal recovery technique, it is characterised in that institute First-stage reverse osmosis film is stated for polyamide reverse osmose membrane.
7. a kind of electroplating rinse water circulating and recovering according to claim 6 and heavy metal recovery technique, it is characterised in that institute Two-pass reverse osmosis film is stated for nanometer silicon carbide complex reverse osmosis membrane;The preparation method of the nanometer silicon carbide complex reverse osmosis membrane For:Nanometer silicon carbide particle is pressed (0.001-0.01):(3-10) weight ratio is added in nitric acid ethyl ammonium salt solution, is made described Nanometer silicon carbide even particulate dispersion is in nitric acid diethyl ammonium solution, then porous support membrane is immersed in solution, carries out heat Process, that is, obtain nanometer silicon carbide complex reverse osmosis membrane.
CN201611064717.8A 2016-11-28 2016-11-28 A kind of electroplating rinse water circulating and recovering and heavy metal recovery technique Expired - Fee Related CN106495379B (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106929683A (en) * 2017-04-07 2017-07-07 环境保护部华南环境科学研究所 The online resource retracting device of thallium in a kind of smelting ore deposit furnace gas
CN107670509A (en) * 2017-11-08 2018-02-09 许锦璐 The household reverse osmosis water purifier and method of two-pass reverse osmosis are integrated with cleaning function
CN112028347A (en) * 2019-06-04 2020-12-04 核工业理化工程研究院 Zero-discharge treatment system and treatment method for chemical nickel plating wastewater

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
RU2088537C1 (en) * 1993-11-04 1997-08-27 Акционерное общество открытого типа завод "Красное знамя" Method of recuperation reverse-osmosis purification of waste water to remove heavy metal ions
CN101481157A (en) * 2008-01-17 2009-07-15 刘寅 Process for advanced treatment of electroplating waste by integrated membrane
CN102020385A (en) * 2010-11-29 2011-04-20 广州凯膜过滤设备有限公司 Method for treating electroplate rinsing wastewater
CN203112630U (en) * 2013-03-25 2013-08-07 西安德奇水处理有限公司 Recovery device for metals in electroplating wastewater
CN104129830A (en) * 2013-05-03 2014-11-05 中国科学院生态环境研究中心 Photoelectrocatalytic method for treating heavy metal complex waste water and recovering heavy metal therefrom

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
RU2088537C1 (en) * 1993-11-04 1997-08-27 Акционерное общество открытого типа завод "Красное знамя" Method of recuperation reverse-osmosis purification of waste water to remove heavy metal ions
CN101481157A (en) * 2008-01-17 2009-07-15 刘寅 Process for advanced treatment of electroplating waste by integrated membrane
CN102020385A (en) * 2010-11-29 2011-04-20 广州凯膜过滤设备有限公司 Method for treating electroplate rinsing wastewater
CN203112630U (en) * 2013-03-25 2013-08-07 西安德奇水处理有限公司 Recovery device for metals in electroplating wastewater
CN104129830A (en) * 2013-05-03 2014-11-05 中国科学院生态环境研究中心 Photoelectrocatalytic method for treating heavy metal complex waste water and recovering heavy metal therefrom

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106929683A (en) * 2017-04-07 2017-07-07 环境保护部华南环境科学研究所 The online resource retracting device of thallium in a kind of smelting ore deposit furnace gas
CN107670509A (en) * 2017-11-08 2018-02-09 许锦璐 The household reverse osmosis water purifier and method of two-pass reverse osmosis are integrated with cleaning function
CN107670509B (en) * 2017-11-08 2020-07-28 许锦璐 Household reverse osmosis water purifier with cleaning function and integrated secondary reverse osmosis and method
CN112028347A (en) * 2019-06-04 2020-12-04 核工业理化工程研究院 Zero-discharge treatment system and treatment method for chemical nickel plating wastewater

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