CN107352680A - A kind of method that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system - Google Patents

A kind of method that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system Download PDF

Info

Publication number
CN107352680A
CN107352680A CN201710576845.9A CN201710576845A CN107352680A CN 107352680 A CN107352680 A CN 107352680A CN 201710576845 A CN201710576845 A CN 201710576845A CN 107352680 A CN107352680 A CN 107352680A
Authority
CN
China
Prior art keywords
heavy metal
surfactant
foam
waste water
wastewater
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.)
Granted
Application number
CN201710576845.9A
Other languages
Chinese (zh)
Other versions
CN107352680B (en
Inventor
李英
张凯
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.)
Shandong University
Original Assignee
Shandong University
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 Shandong University filed Critical Shandong University
Priority to CN201710576845.9A priority Critical patent/CN107352680B/en
Priority to PCT/CN2017/104317 priority patent/WO2019010835A1/en
Publication of CN107352680A publication Critical patent/CN107352680A/en
Application granted granted Critical
Publication of CN107352680B publication Critical patent/CN107352680B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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
    • C02F1/58Treatment of water, waste water, or sewage by removing specified dissolved compounds
    • C02F1/62Heavy metal 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
    • 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
    • C02F2301/00General aspects of water treatment
    • C02F2301/08Multistage treatments, e.g. repetition of the same process step under different conditions

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Removal Of Specific Substances (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

The present invention relates to a kind of method that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system, this method includes:The pH for adjusting waste water is 4 11, and surfactant solution is added into waste water, the mol ratio of surfactant and all heavy metal ion total mole numbers in waste water is proper proportion and is stirred;Foregoing mixed liquor is introduced into foam processor, foamed gas are passed through with certain gas flow rate through quartzy core in foam processor bottom, the foam of generation is introduced into foam trap the recycling for carrying out defoaming and heavy metal by foam processor top duct, until non-foam produces.The measure of concentration of heavy metal ion is carried out to the water after processing, the clearance of this method heavy metal ion can reach more than 99%.Secondary pollution is not caused to water body, contaminated waste water is reached the effect of thorough heavy-metal ion removal.

Description

It is a kind of that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system Method
Technical field
The present invention relates to a kind of method that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system, category In Environmental Chemistry technical field.
Background technology
With the fast development of economy, domestic and international water pollution is on the rise, wherein, the pollution sources Battery Plant containing heavy metal Water resource is caused greatly to destroy for waste water and pollution, while influences pole to agricultural, industry, human lives and the whole ecological balance Greatly.Battery Plant's waste water, which not only dissipates, derives soil and atmosphere pollution, and can seriously endanger animals and humans by food chain Life and health.Waste water main source in battery production, which has in the waste water of production line for manufacturing battery cleaning slurry, allotment slurry, to be spilt leakage Medicament waste water, cleaning produce the waste water on ground etc., contain substantial amounts of Pb2+,Zn2+,Mn2+,Hg2+Etc. heavy metal ion.These huge sum of moneys Category ion will not be weakened or be disappeared by biodegradable and biological chain circulation, be enriched with put easily in biological chain on the contrary Greatly, it is present in for a long time in organism, and the toxicity of heavy metal is larger, therefore the existence to the mankind is healthy and Environmental security causes Serious influence, harm are very big.Therefore, efficient quick pollution control of water, the particularly improvement to Battery Plant's pollutant effluents, tool There are important environmental effect and far-reaching social effect.
The control measures of heavy metal pollution can be largely classified into Physical, chemical method, life by its mechanism of action in water at present Thing method etc..Physical includes extraction, absorption method, ion-exchange, UF membrane etc., the heavy metal ion in waste water is not changed Adsorbed, concentrated, separated under chemical form;Such method efficiency high, but Meteorological height be present, quantities is big, is easily introduced The shortcomings of pollution source.Bioanalysis is mainly made a return journey in depollution water body by the absorption enrichment of plant, microorganism Heavy metal ion, but because its action period is grown, treating capacity is small, the plant treatment difficulty after heavy metal ion is adsorbed, to metal The recovery utilization rate of ion is low to wait short slab also to govern its popularization in commercial Application.Chemical method generally by additive with The effect heavy-metal ion removals such as heavy metal ion generation oxidation, reduction, precipitation, absorption, suppression, wherein the precipitation method are because of economy It is good, applied widely, turn into and most processing methods is applied in Battery Plant's wastewater treatment, by adding hydroxide, sulfide And have the chelating agent or complex compound of stronger combination with heavy metal ion, form not soluble in water sink with heavy metal ion Form sediment, and then the purpose of purifying water body.But for the industrial wastewater of complicated component, because each ion precipitation scope is different, often Need repeatedly to adjust pH or repeatedly add different types of agent in batches, not only complex operation, and inefficient, sink The processing of starch is there is also difficulty, if dealing with improperly, easy reactivation, can cause secondary pollution, it is difficult to reach national discharge Standard.
The content of the invention
In view of the shortcomings of the prior art, the present invention is provided one kind and thoroughly removed in Battery Plant's waste water using water based foam system The method of heavy metal ion.The present invention forms water base foam using green specific surfactant, and the surface of selection is lived Property agent and Pb2+, Zn2+It is positive with metal with electrically interaction or complexing, surfactant molecule etc. between heavy metal ion After ion is combined closely, using the amphipathic absorption of surfactant on gas-liquid interface, by the bubble of floating by heavy metal Ion takes polluted-water out of.The present invention is simple to operate, and cost is cheap, and surfactant concentration is low, to Battery Plant's waste water Complexity is adaptable, and removal efficiency is high, suitable for the removal of contents of many kinds of heavy metal ion, and passes through preferred environmental type Surfactant, it is ensured that do not have secondary pollution to environment.
Technical scheme is as follows:
A kind of method that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system, including step is such as Under:
(1) pH for adjusting waste water is 4-11, and the surfactant solution prepared in advance, surface-active are added into waste water The addition of agent solution makes the mol ratio of surfactant and all heavy metal ion total mole numbers in waste water be (1~50):1, Stir;
(2) mixed liquor that step (1) obtains is introduced into foam processor, foaming gas is passed through in foam processor bottom Body, the control of foamed gas air velocity introduce foam in 0.1~1.0L/min, generation foam by foam processor top duct Defoaming and the recycling of heavy metal are carried out in collector, until non-foam produces.
According to currently preferred, the surfactant described in step (1) is at least to contain an electronegative polarity Hydrophilic radical, the surfactant that hydrophobic group carbon chain lengths are 8-24, described negatively charged polar hydrophilic group are sulfate, sulphur Acidic group or carboxylic acid group.
It is further preferred that described surfactant also contains EO, carbonyl or amide group.
According to currently preferred, described surfactant be alkyl sulfate, fatty alcohol polyoxyethylene ether sulfate, Alkyl carboxylate or the one of which in alkyl, polyether carboxylate or two or more any mixing.
It is further preferred that the surfactant containing sulfate is lauryl sodium sulfate or AEO Sodium sulphate.
It is further preferred that the surfactant containing carboxylic acid group is sodium laurate or trideceth -4- Carboxylic acid sodium.
According to currently preferred, surfactant and all heavy metal ion total mole numbers in waste water in step (1) Mol ratio is (1~30):1, it is preferred that the mol ratio of surfactant and all heavy metal ion total mole numbers in waste water is (3 ~15):1, highly preferred, the mol ratio of surfactant and all heavy metal ion total mole numbers in waste water is (5~7): 1。
According to currently preferred, the pH of waste water is 5-11 in step (1).
According to currently preferred, foamed gas air velocity is 0.1~0.7L/min in step (2), further preferably , foamed gas air velocity is 0.2~0.6L/min.
According to currently preferred, foamed gas are N in step (2)2Or air.
According to currently preferred, the underfill of foam processor has porous media quartz sand, porous Jie in step (2) Matter quartz sand porosity is 35-45%, and average pore throat radius is 0.1-10 μm, packed height 4-7mm.
For percentage of batteries factory heavy metals ion concentration greatly or mixed liquor be in highly acid situation, carry out foam First waste water can be pre-processed before separation, i.e., adjust the pH of waste water to weak acid or neutrality by adding appropriate aqueous slkali, and To caused precipitation filtering.It need not be pre-processed if waste water is without features described above.It is divided after being disposed using NITRATE BY FLAME ATOMIC Photometer carries out the measure of concentration of heavy metal ion to remaining water body, calculates the removal efficiency of heavy metal ion.
The method detailed process that the present invention removes Battery Plant's heavy metal ions in wastewater using water base foam is summarized as follows:
Collect the species and content of wastewater sample analysis wherein heavy metal element, then according to the heavy metal in waste water from The mol ratio of son is (1~50):1 ratio, and wanted with the mixed overall molar concentration of waste water for (1~15) mmol/L Ask, weighing surfactant is some, mixes with appropriate pure water, in the case of 25~40 DEG C of constant temperature, stirs, and forms surface Activator solution, after inorganic agent added into waste water, be suitably uniformly mixed.Then mixed liquor is introduced into foam processor, together When gas is introduced from foam processor, air velocity is controlled in 0.1~1.0L/min using gas flowmeter, at foam The drainage system on reason device top is introduced a foam into foam trap, carries out defoaming and the recovery of heavy metal.Gas is persistently injected, Untill non-foam produces.
The principle of the present invention:
The present invention uses and Pb2+, Zn2+Etc. the specific surfactant between heavy metal ion with interaction, surface is lived Property agent molecule is combined closely in aqueous with metal cation, after introducing a gas into solution, due to the amphiphilic of surfactant Property will adsorb on the gas-liquid interface of bubble, being floated by density variation to form foam, takes heavy metal ion out of polluted-water.
Advantages of the present invention is as follows:
1st, method of the invention can thoroughly remove the Pb being enriched with Battery Plant's waste water2+, Zn2+Etc. heavy metal ion, quickly Efficiently, input is low, and power consumption is few, and operation is simple.
2nd, the inventive method is in processing Pb2+, Zn2+Application in terms of the Battery Plant's waste water polluted etc. heavy metal ion, surface Activating agent dosage is few, removal of heavy metal ions efficiency high, to Pb in waste water2+、Zn2+Removal efficiency can reach 99.8 with Upper %, does not cause secondary pollution to water body, reaches the effect of thorough heavy-metal ion removal.
3rd, method of the invention, the various Battery Plant's waste water polluted by heavy metal ion are may be directly applied to, reaches preferable Removal efficiency, meet discharging standards.
4th, method of the invention, departs from the foam of aqueous phase, and after processing, heavy metal element can reclaim, while surface is lived Property agent can also recycle.
By carrying out the measure of concentration of heavy metal ion to water body before and after the processing, removal efficiency is calculated.Removal efficiency η= (C1-C2)/C1, wherein C1It is the concentration of before processing heavy metal ion, C2It is the concentration that foaming terminates rear remaining heavy metal ion.Go Except the type of the hydrophilic radical of the influence factor including surfactant of efficiency, the mol ratio of surfactant and metal ion, Air velocity, surfactant solution concentration and body phase pH etc..
Brief description of the drawings
Fig. 1 is foamed gas air velocity to Pb2+、Zn2+The influence curve figure of removal efficiency.
Embodiment
With reference to embodiment, the present invention will be further described, but is not limited only to this.
Embodiment 1:
A kind of method that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system, in pending waste water Pb2+Concentration be 0.5mmol/L, solution is in faintly acid, and pH 4, step is as follows:
(1) waste water is in faintly acid, and without pretreatment, lauryl sodium sulfate, which is dissolved in water, is configured to lauryl sodium sulfate Solution is added in waste water, it is well mixed after in waste water the overall density of lauryl sodium sulfate be 3.5mmol/L, dodecyl sulphur Sour sodium and Pb2+Mol ratio is 7:1;
(2) mixed liquor that step (1) obtains is introduced into the foam processor that underfill has porous media quartz sand, Foam processor bottom is passed through N2, air velocity 0.1L/min, persistently foam untill it can not produce foam, foam passes through The pipeline on treating column top is introduced in foam trap, is recycled as surfactant and heavy metal removal.Then again The analysis that concentration of heavy metal ion is carried out to the water reuse NITRATE BY FLAME ATOMIC spectrophotometer after processing determines, and calculates removal efficiency η=(C1-C2)/C1, as a result show that this method removes Pb2+Efficiency be 99.8%.
Embodiment 2:
A kind of method that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system, in pending waste water Pb2+And Zn2+Concentration is respectively 0.2mmol/L, and 0.3mmol/L, solution is in neutrality, and pH 6.82, step is as follows:
(1) waste water is in neutrality, and without pretreatment, trideceth -4- carboxylic acid sodiums, which are dissolved in water, is configured to tridecanol Polyethers -4- carboxylic acids sodium solution is added in waste water, is well mixed the overall density of trideceth -4- carboxylic acid sodiums in rear waste water For 2.5mmol/L, trideceth -4- carboxylic acid sodiums and Pb2+And Zn2+The mol ratio of total mole number is 5:1;
(2) mixed liquor that step (1) obtains is introduced into the foam processor that underfill has porous media quartz sand, Foam processor bottom is passed through N2, air velocity 0.2L/min, persistently foam untill it can not produce foam, foam passes through The pipeline on treating column top is introduced in foam trap, is recycled as surfactant and heavy metal removal.Then again The analysis that concentration of heavy metal ion is carried out to the water reuse NITRATE BY FLAME ATOMIC spectrophotometer after processing determines, and calculates removal efficiency η=(C1-C2)/C1, as a result show that this method removes Pb2+、Zn2+Efficiency can reach more than 99.9 %.
Embodiment 3:
A kind of method that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system, pending waste water are dilute Release rear Pb2+And Zn2+Concentration is respectively 0.3mmol/L, and 0.7mmol/L, solution is in faintly acid, and pH 5, step is as follows:
(1) waste water is in faintly acid, and without pretreatment, trideceth -4- carboxylic acid sodiums, which are dissolved in water, is configured to tridecane Alcohol polyethers -4- carboxylic acids sodium solution is added in waste water, is well mixed the overall density of trideceth -4- carboxylic acid sodiums in rear waste water For 5 mmol/L, trideceth -4- carboxylic acid sodiums and Pb2+And Zn2+The mol ratio of total mole number is 5:1;
(2) mixed liquor that step (1) obtains is introduced into the foam processor that underfill has porous media quartz sand, Foam processor bottom is passed through N2, air velocity 0.2L/min, persistently foam untill it can not produce foam, foam passes through The pipeline on treating column top is introduced in foam trap, is recycled as surfactant and heavy metal removal.Then again The analysis that concentration of heavy metal ion is carried out to the water reuse NITRATE BY FLAME ATOMIC spectrophotometer after processing determines, and calculates removal efficiency η=(C1-C2)/C1, as a result show that this method removes Pb2+、Zn2+Efficiency be 99.8%.
Embodiment 4:
A kind of method that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system, pending waste water Pb2+And Zn2+Concentration is respectively 1.0mmol/L, and 1.5mmol/L, solution is in highly acid, and pH 1.2, step is as follows:
(1) waste water is in highly acid, and first Battery Plant's waste water is pre-processed, and prepares 1mmol/L sodium hydroxide solution, is added Waste water is adjusted in waste water to neutrality, pH 7, precipitation is filtered, retains the concentration that filtrate determines heavy metal ion again;Tridecane Alcohol polyethers -4- carboxylic acid sodiums and lauryl sodium sulfate, which are dissolved in water, to be configured in solution addition waste water, after being well mixed in waste water The total concentration of trideceth -4- carboxylic acid sodiums and lauryl sodium sulfate is 12mmol/L, trideceth -4- carboxylic acid sodiums With lauryl sodium sulfate and Pb2+And Zn2+The mol ratio of total mole number is 5:1;
(2) mixed liquor that step (1) obtains is introduced into the foam processor that underfill has porous media quartz sand, Foam processor bottom is passed through N2, air velocity 0.3L/min, persistently foam untill it can not produce foam, foam passes through The pipeline on treating column top is introduced in foam trap, is recycled as surfactant and heavy metal removal.Then again The analysis that concentration of heavy metal ion is carried out to the water reuse NITRATE BY FLAME ATOMIC spectrophotometer after processing determines, and calculates removal efficiency η=(C1-C2)/C1, as a result show that this method removes Pb2+、Zn2+Efficiency reach more than 99.8%.
Comparative example
The method for thoroughly removing Battery Plant's heavy metal ions in wastewater using water based foam system as described in Example 1, Difference is:
Comparative example 1:Air velocity is 0.01L/min.
Comparative example 2:Air velocity is 0.05L/min.
Comparative example 3:Air velocity is 0.08L/min.
Comparative example 4:Air velocity is 1.2L/min.
Comparative example 5:Air velocity is 1.4L/min.
Comparative example 6:Air velocity is 1.6L/min.
Comparative example 7:Air velocity is 2.0L/min.
Experimental example:
The processing method difference foamed gas air velocity of above-described embodiment 1~4 and comparative example 1~7 is to Pb2+、Zn2+Go Except Fig. 1 is shown in the influence of efficiency.(wherein, surfactant concentration 3.5mmol/L, lead ion, zinc ion concentration are respectively 0.5mmol/L, pH value of solution 6).

Claims (10)

1. a kind of method that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system, including step are as follows:
(1) pH for adjusting waste water is 4-11, the surfactant solution prepared in advance is added into waste water, surfactant is molten The addition of liquid makes the mol ratio of surfactant and all heavy metal ion total mole numbers in waste water be (1~50):1, stirring Uniformly;
(2) mixed liquor that step (1) obtains is introduced into foam processor, foamed gas is passed through in foam processor bottom, sent out Gas flow speed control is steeped to introduce foam in 0.1~1.0L/min, generation foam by foam processor top duct and collect Defoaming and the recycling of heavy metal are carried out in device, until non-foam produces.
2. the side according to claim 1 that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system Method, it is characterised in that the surfactant described in step (1) is at least containing an electronegative polar hydrophilic group, dredged Water base carbon chain lengths are 8-24 surfactant, and described negatively charged polar hydrophilic group is sulfate, sulfonic group or carboxylic acid Base.
3. the side according to claim 2 that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system Method, it is characterised in that described surfactant also contains EO, carbonyl or amide group.
4. the side according to claim 2 that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system Method, it is characterised in that described surfactant is alkyl sulfate, fatty alcohol polyoxyethylene ether sulfate, alkyl carboxylate Or the one of which in alkyl, polyether carboxylate or two or more any mixing.
5. the side according to claim 2 that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system Method, it is characterised in that the surfactant containing sulfate is lauryl sodium sulfate or sodium sulfate of polyethenoxy ether of fatty alcohol.
6. the side according to claim 2 that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system Method, it is characterised in that the surfactant containing carboxylic acid group is sodium laurate or trideceth -4- carboxylic acid sodiums.
7. the side according to claim 1 that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system Method, it is characterised in that in step (1) in surfactant and waste water all heavy metal ion total mole numbers mol ratio for (1~ 30):1, it is preferred that the mol ratio of surfactant and all heavy metal ion total mole numbers in waste water is (3~15):1, the most Preferably, the mol ratio of surfactant and all heavy metal ion total mole numbers in waste water is (5~7):1, the pH of waste water are 5-11。
8. the side according to claim 1 that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system Method, it is characterised in that foamed gas air velocity is 0.1~0.7L/min in step (2), it is further preferred that foamed gas Air velocity is 0.2~0.6L/min.
9. the side according to claim 1 that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system Method, it is characterised in that foamed gas are N in step (2)2Or air.
10. the side according to claim 1 that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system Method, it is characterised in that the underfill of foam processor has porous media quartz sand, porous media quartz sand hole in step (2) Gap rate is 35-45%, and average pore throat radius is 0.1-10 μm, packed height 4-7mm.
CN201710576845.9A 2017-07-14 2017-07-14 Method for thoroughly removing heavy metal ions in wastewater of battery plant by using water-based foam system Active CN107352680B (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
CN201710576845.9A CN107352680B (en) 2017-07-14 2017-07-14 Method for thoroughly removing heavy metal ions in wastewater of battery plant by using water-based foam system
PCT/CN2017/104317 WO2019010835A1 (en) 2017-07-14 2017-09-29 Method for completely removing heavy metal ions in battery plant wastewater by using water-based foam system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710576845.9A CN107352680B (en) 2017-07-14 2017-07-14 Method for thoroughly removing heavy metal ions in wastewater of battery plant by using water-based foam system

Publications (2)

Publication Number Publication Date
CN107352680A true CN107352680A (en) 2017-11-17
CN107352680B CN107352680B (en) 2020-04-21

Family

ID=60292971

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710576845.9A Active CN107352680B (en) 2017-07-14 2017-07-14 Method for thoroughly removing heavy metal ions in wastewater of battery plant by using water-based foam system

Country Status (2)

Country Link
CN (1) CN107352680B (en)
WO (1) WO2019010835A1 (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108658204A (en) * 2018-06-07 2018-10-16 厦门大学 Application of the soapberry extract in foam fraction factor harvests nickel ion
CN109081393A (en) * 2018-08-27 2018-12-25 北京中晟清源环保科技有限公司 A kind of new-type air-floatation auxiliary agent and preparation method
CN109721147A (en) * 2019-02-27 2019-05-07 郑州大学 Metal ion and the method for preparing lithium ion battery negative material in a kind of recycling waste water
CN109809518A (en) * 2019-03-06 2019-05-28 广州大学 A kind of device of froth flotation method processing waste water containing thallium
CN112427451A (en) * 2020-11-20 2021-03-02 山东大学 Water-based foam system and method for simultaneously removing heavy metals and organic pollutants in soil

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106587273A (en) * 2017-01-05 2017-04-26 扬州大学 Method for biosurfactant micelle enhanced ultrafiltration treatment of heavy metal wastewater

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6635182B1 (en) * 2001-05-04 2003-10-21 Industrial Waste Water Services, Llp Floatation process for removal of heavy metal waste and associated apparatus
CN100378007C (en) * 2006-04-30 2008-04-02 湖南大学 Method for treating cadmium-containing waste water by intensified ultrafiltration of hollow fiber ultrafiltration membrane and foam floatation
KR20120069895A (en) * 2010-12-21 2012-06-29 재단법인 포항산업과학연구원 Treatment method for wastewater including heavy metal and treatment apparatus thereof
CN107055666A (en) * 2017-06-06 2017-08-18 陕西理工大学 The apparatus and method of contents of many kinds of heavy metal ion in a kind of efficient process waste water

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106587273A (en) * 2017-01-05 2017-04-26 扬州大学 Method for biosurfactant micelle enhanced ultrafiltration treatment of heavy metal wastewater

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
汪德进等: "连续式泡沫浮选法处理含铬废水研究", 《中国卫生检验杂志》 *
董红星等: "《新型传质分离技术基础》", 31 May 2005 *

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108658204A (en) * 2018-06-07 2018-10-16 厦门大学 Application of the soapberry extract in foam fraction factor harvests nickel ion
CN109081393A (en) * 2018-08-27 2018-12-25 北京中晟清源环保科技有限公司 A kind of new-type air-floatation auxiliary agent and preparation method
CN109721147A (en) * 2019-02-27 2019-05-07 郑州大学 Metal ion and the method for preparing lithium ion battery negative material in a kind of recycling waste water
CN109809518A (en) * 2019-03-06 2019-05-28 广州大学 A kind of device of froth flotation method processing waste water containing thallium
CN112427451A (en) * 2020-11-20 2021-03-02 山东大学 Water-based foam system and method for simultaneously removing heavy metals and organic pollutants in soil

Also Published As

Publication number Publication date
CN107352680B (en) 2020-04-21
WO2019010835A1 (en) 2019-01-17

Similar Documents

Publication Publication Date Title
CN107352680A (en) A kind of method that Battery Plant's heavy metal ions in wastewater is thoroughly removed using water based foam system
CN103771650B (en) A kind for the treatment of process of coal gasification waste water
CN104310672B (en) Waste water containing thallium Strong oxdiative coagulation and adsorption recovery process
CN102234160B (en) Method for treating low-concentration arsenic-containing wastewater
CN100390081C (en) Process method for waste water containing nitrobenzene and aniline
CN107473466B (en) Treatment method of beneficiation wastewater
CN103951114B (en) A kind of heavy metal wastewater thereby tertiary treatment and deep purifying reuse technology
CN104193043B (en) A kind of high concentration alkaline waste water containing arsenic dearsenification treatment process and method
CN102234161B (en) Method for treating high-concentration arsenic-containing wastewater
CN208471815U (en) A kind of high-concentration sewage treatment system of AO technique and Fenton system support
CN109354321A (en) A kind of recycling processing system and its processing method of pharmacy waste water
CN110078332A (en) A method of promoting excess sludge anaerobic fermentation and acid production using modified steel scoria
CN103351051B (en) Method for removing organic pollutants in waste water by taking Ca(OH)2 as catalyst of ozone
CN106315973A (en) Treatment method of high-salt and high-calcium industrial wastewater
CN106186559A (en) The processing method of high-sulfate height Organic substance industrial wastewater
CN110407359A (en) One kind adopting beneficiation wastewater treatment method
CN109879512A (en) Method for treating garbage percolation liquid based on ceramic membrane
CN105923911A (en) Refuse leachate pretreatment method
CN107857434A (en) A kind of handling process of wet flue gas desulfurization waste water
CN108046484A (en) A kind of device and method using solid phase class Fenton process processing desulfurization wastewater
CN104986898B (en) A kind of method and device of normal temperature ferrite circular treatment heavy metal containing sewage
CN104761039A (en) Composite chelating agent used for treating cadmium-containing waste water and application method thereof
CN110436661A (en) A kind of method and apparatus removing surfactant in water removal using foam enrichment
CN207079100U (en) A kind of combined treatment process system of waste water containing various heavy
CN106746373B (en) Process for removing chemicals in beer wastewater

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant