CN112403028A - Method for purifying lead electrolyte by using columnar activated carbon - Google Patents

Method for purifying lead electrolyte by using columnar activated carbon Download PDF

Info

Publication number
CN112403028A
CN112403028A CN202010817378.6A CN202010817378A CN112403028A CN 112403028 A CN112403028 A CN 112403028A CN 202010817378 A CN202010817378 A CN 202010817378A CN 112403028 A CN112403028 A CN 112403028A
Authority
CN
China
Prior art keywords
activated carbon
lead electrolyte
desorption
exchange column
purified
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.)
Pending
Application number
CN202010817378.6A
Other languages
Chinese (zh)
Inventor
许化龙
彭志平
雷日华
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.)
Chenzhou Xiongfeng Environmental Protection Science And Technology Co ltd
Original Assignee
Chenzhou Xiongfeng Environmental Protection Science And Technology Co ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Chenzhou Xiongfeng Environmental Protection Science And Technology Co ltd filed Critical Chenzhou Xiongfeng Environmental Protection Science And Technology Co ltd
Priority to CN202010817378.6A priority Critical patent/CN112403028A/en
Publication of CN112403028A publication Critical patent/CN112403028A/en
Pending legal-status Critical Current

Links

Images

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D15/00Separating processes involving the treatment of liquids with solid sorbents; Apparatus therefor
    • B01D15/08Selective adsorption, e.g. chromatography
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D15/00Separating processes involving the treatment of liquids with solid sorbents; Apparatus therefor
    • B01D15/08Selective adsorption, e.g. chromatography
    • B01D15/10Selective adsorption, e.g. chromatography characterised by constructional or operational features
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D15/00Separating processes involving the treatment of liquids with solid sorbents; Apparatus therefor
    • B01D15/08Selective adsorption, e.g. chromatography
    • B01D15/10Selective adsorption, e.g. chromatography characterised by constructional or operational features
    • B01D15/20Selective adsorption, e.g. chromatography characterised by constructional or operational features relating to the conditioning of the sorbent material
    • B01D15/203Equilibration or regeneration
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/34Regenerating or reactivating
    • B01J20/3416Regenerating or reactivating of sorbents or filter aids comprising free carbon, e.g. activated carbon
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/34Regenerating or reactivating
    • B01J20/345Regenerating or reactivating using a particular desorbing compound or mixture
    • B01J20/3475Regenerating or reactivating using a particular desorbing compound or mixture in the liquid phase
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/283Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
    • 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
    • C25ELECTROLYTIC OR ELECTROPHORETIC PROCESSES; APPARATUS THEREFOR
    • C25CPROCESSES FOR THE ELECTROLYTIC PRODUCTION, RECOVERY OR REFINING OF METALS; APPARATUS THEREFOR
    • C25C1/00Electrolytic production, recovery or refining of metals by electrolysis of solutions
    • C25C1/18Electrolytic production, recovery or refining of metals by electrolysis of solutions of lead
    • CCHEMISTRY; METALLURGY
    • C25ELECTROLYTIC OR ELECTROPHORETIC PROCESSES; APPARATUS THEREFOR
    • C25CPROCESSES FOR THE ELECTROLYTIC PRODUCTION, RECOVERY OR REFINING OF METALS; APPARATUS THEREFOR
    • C25C7/00Constructional parts, or assemblies thereof, of cells; Servicing or operating of cells
    • C25C7/06Operating or servicing
    • 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
    • C02F2303/00Specific treatment goals
    • C02F2303/16Regeneration of sorbents, filters

Abstract

The invention discloses a method for purifying lead electrolyte by using columnar activated carbon, which relates to the technical field of purifying lead electrolyte by using activated carbon, in particular to a method for purifying lead electrolyte by using columnar activated carbon, and comprises the following steps: s1, purifying lead electrolyte; s2, desorbing and regenerating the active carbon exchange column group; s3, neutralizing and recycling the waste water. The method for purifying the lead electrolyte by using the columnar activated carbon adopts the activated carbon adsorption exchange column group for purification, has simple operation, does not need other auxiliary reagents, and generally needs desorption regeneration for three months after the activated carbon exchange column group works for a period of time; adsorbing substances in the solution to be separated by using active carbon; calcium chloride is used as a desorption agent for desorption and regeneration of the activated carbon; CaCl2 is selected as a desorption agent, so that the adsorption stability of the activated carbon on the adsorbate can be reduced, and the aim of reducing desorption activation energy is fulfilled; the ions such as bismuth and antimony absorbed in the activated carbon are eluted through desorption operation, and the carbon column is washed by purified water to achieve the purpose of activated carbon regeneration.

Description

Method for purifying lead electrolyte by using columnar activated carbon
Technical Field
The invention relates to the technical field of purifying lead electrolyte by activated carbon, in particular to a method for purifying lead electrolyte by using columnar activated carbon.
Background
In the electrolytic refining of the lead bullion, the lead bullion anode usually contains impurities such as gold, silver, copper, antimony, arsenic, tin, bismuth and the like, and during the electrolytic refining process, metals with a potential negative than that of the lead, such as zinc, iron, cadmium, cobalt, nickel and the like, contained in the anode are dissolved out from the anode together with the lead, but are not generally precipitated at the cathode; metals with positive potential than lead, such as antimony, bismuth, copper, gold and the like, hardly enter the electrolyte and are left in the anode mud; in actual production, a small amount of the metal ions enter the electrolyte, particularly bismuth, and main impurities forming electrolytic lead are separated out at the cathode under the action of electrophoresis.
In order to recover lead and silicofluoric acid in the anode slime, the anode slime is washed by water, and the impurity content of the lead electrolyte is ultrahigh due to the fact that the washing water of the anode slime contains high bismuth and antimony.
In order to purify the lead electrolyte and ensure the normal operation of the lead electrolysis process and the quality of the electrolytic lead, the harmful impurities such as bismuth, copper, antimony, silver and the like in the lead electrolyte must be continuously removed.
For purifying the lead electrolyte, various purification methods can be used, such as a chemical method, an activated carbon adsorption method, an extraction method, an ion exchange method, and the like. The chemical method adds other reagents and introduces impurities, and has the disadvantages of long process flow, high energy consumption and environmental pollution caused by organic solvents in the extraction method and the ion exchange process.
Disclosure of Invention
Aiming at the defects of the prior art, the invention provides a method for purifying lead electrolyte by using columnar activated carbon, which solves the problem that in the prior art, a small amount of metal ions, particularly bismuth, enter the electrolyte in actual production and are precipitated at a cathode under the action of electrophoresis to form main impurities of electrolytic lead.
In order to achieve the purpose, the invention is realized by the following technical scheme: the method for purifying the lead electrolyte by using the columnar activated carbon comprises the following steps:
s1, lead electrolyte purification: opening a liquid storage tank valve of lead electrolyte to be purified, starting an anti-corrosion pump and related valves, controlling the flow rate to be 50L/min, enabling the lead electrolyte to be purified to enter an activated carbon exchange column group, sampling and analyzing harmful impurities such as bismuth, antimony and the like in the lead electrolyte to be purified after the lead electrolyte to be purified completely passes through the activated carbon exchange column group, taking purified liquid for detection, merging the purified liquid into a lead electrolyte circulating system after the purified liquid meets the requirements, and repeatedly purifying unqualified purified liquid until the purified liquid is qualified;
s2, desorption and regeneration of the activated carbon exchange column group: the active carbon exchange column group is required to be desorbed and regenerated after running for about three months; during desorption operation, lead electrolyte containing harmful impurities such as bismuth, antimony and the like to be purified passes through a columnar active carbon exchange column group to adsorb harmful impurity ions in the lead electrolyte to be purified, calcium chloride liquid is added into a desorption agent box, 6-10g/L of calcium chloride is controlled, an anticorrosion pump and a relevant valve are opened to carry out desorption, pure water is added into the desorption agent box to wash the exchange column for three times after desorption is completed, and purification operation can be carried out after washing is completed;
s3, neutralizing and recycling wastewater: and pumping the desorption solution and the washing solution to a wet workshop for neutralization and precipitation, recovering valuable elements in the solution, and delivering the waste solution to a sewage station for disposal.
Optionally, in the step S1, during the purification of the lead electrolyte, the activated carbon exchange column group is formed by connecting three activated carbon exchange columns in series, the activated carbon exchange columns are made of organic glass, and the height-diameter ratio is 5: 1.
optionally, the exchange column is connected by transparent high-pressure plastic hose, and the hose diameter is 50mm, and pumping power is anticorrosive pump, and the power of pump motor is 5.5 KW.
Optionally, the activated carbon in the activated carbon exchange column group is columnar coconut shell activated carbon.
Optionally, in the step S1 and the lead electrolyte purification, the purification mode is a dynamic mode.
Optionally, the dynamic mode is that the lead electrolyte to be purified is pumped into the activated carbon exchange column group by an anticorrosive pump, the flow rate is controlled to be 50L/min, the lead electrolyte to be purified completely passes through the activated carbon exchange column group, then, the lead electrolyte is sampled and analyzed for harmful impurities such as bismuth, antimony and the like, and the lead electrolyte can be merged into the lead electrolyte circulating system after being qualified.
Optionally, in step S2 and the desorption and regeneration of the activated carbon exchange column group, the activated carbon desorption and regeneration system shares the anticorrosion pump, and the desorption agent is contained in the desorption agent box which is specially manufactured and is connected with the outlet pipe diameter of the anticorrosion pump through a tee joint and a valve.
The invention provides a method for purifying lead electrolyte by using columnar activated carbon, which has the following beneficial effects:
the invention relates to a lead electrolyte purification method, which comprises the steps of contacting electrolyte containing impurities such as bismuth and antimony to be purified with columnar carbon, adsorbing the impurities such as bismuth and antimony by the activated carbon, and regenerating the activated carbon by using calcium chloride as a desorption agent after the activated carbon is used for three months. The method has the advantages of friendly operation environment, low energy consumption, recyclable regenerated columnar activated carbon, low cost, no change of the main components of the lead electrolyte and direct utilization of the purified electrolyte;
the purification by adopting the activated carbon adsorption exchange column group has simple operation and does not need other auxiliary reagents, and the activated carbon adsorption exchange column group generally needs to be desorbed and regenerated for three months after working for a period of time; adsorbing substances in the solution to be separated by using active carbon; calcium chloride is used as a desorption agent for desorption and regeneration of the activated carbon; CaCl2 is selected as a desorption agent, so that the adsorption stability of the activated carbon on the adsorbate can be reduced, and the aim of reducing desorption activation energy is fulfilled; the ions such as bismuth and antimony absorbed in the activated carbon are eluted through desorption operation, and the carbon column is washed by purified water to achieve the purpose of activated carbon regeneration.
Drawings
FIG. 1 is a schematic diagram of the process steps of the present invention;
FIG. 2 is a simplified flow chart of the present invention.
Detailed Description
The technical solutions in the embodiments of the present invention will be clearly and completely described below with reference to the drawings in the embodiments of the present invention, and it is obvious that the described embodiments are only a part of the embodiments of the present invention, and not all of the embodiments.
Referring to fig. 1 to 2, the present invention provides a technical solution: the method for purifying the lead electrolyte by using the columnar activated carbon comprises the following steps:
s1, lead electrolyte purification: opening a liquid storage tank valve of lead electrolyte to be purified, starting an anti-corrosion pump and related valves, controlling the flow rate to be 50L/min, enabling the lead electrolyte to be purified to enter an activated carbon exchange column group, sampling and analyzing harmful impurities such as bismuth, antimony and the like in the lead electrolyte to be purified after the lead electrolyte to be purified completely passes through the activated carbon exchange column group, taking purified liquid for detection, merging the purified liquid into a lead electrolyte circulating system after the purified liquid meets the requirements, and repeatedly purifying unqualified purified liquid until the purified liquid is qualified;
s2, desorption and regeneration of the activated carbon exchange column group: the active carbon exchange column group is required to be desorbed and regenerated after running for about three months; during desorption operation, lead electrolyte containing harmful impurities such as bismuth, antimony and the like to be purified passes through a columnar active carbon exchange column group to adsorb harmful impurity ions in the lead electrolyte to be purified, calcium chloride liquid is added into a desorption agent box, 6-10g/L of calcium chloride is controlled, an anticorrosion pump and a relevant valve are opened to carry out desorption, pure water is added into the desorption agent box to wash the exchange column for three times after desorption is completed, and purification operation can be carried out after washing is completed;
s3, neutralizing and recycling wastewater: and pumping the desorption solution and the washing solution to a wet workshop for neutralization and precipitation, recovering valuable elements in the solution, and delivering the waste solution to a sewage station for disposal.
In the invention:
further, in the step S1, during the purification of the lead electrolyte, the activated carbon exchange column group is composed of three activated carbon exchange columns connected in series, the activated carbon exchange columns are made of organic glass, and the height-diameter ratio is 5: 1.
Furthermore, the exchange column is connected by transparent high-pressure plastic hose, and the hose diameter is 50mm, and pumping power is anticorrosive pump, and the power of pump motor is 5.5 KW.
Furthermore, the active carbon in the active carbon exchange column group is columnar coconut shell active carbon.
5. The method for purifying lead electrolyte using columnar activated carbon as claimed in claim 1, wherein: in the step S1 and the lead electrolyte purification, the purification mode is a dynamic mode.
Furthermore, the lead electrolyte to be purified is pumped into the active carbon exchange column group by an anticorrosive pump in a dynamic mode, the flow rate is controlled to be 50L/min, the lead electrolyte to be purified completely passes through the active carbon exchange column group, then, the lead electrolyte is sampled and analyzed for harmful impurities such as bismuth, antimony and the like in the lead electrolyte, and the lead electrolyte can be merged into a lead electrolyte circulating system after being qualified.
Further, in the desorption regeneration of the activated carbon exchange column group in the step S2, the activated carbon desorption regeneration system shares the anticorrosion pump, and the desorption agent is contained in the desorption agent box which is specially manufactured and is connected with the outlet pipe diameter of the anticorrosion pump through a tee joint and a valve.
In summary, the method for purifying the lead electrolyte by using the columnar activated carbon comprises the steps of opening a valve of a liquid storage tank of the lead electrolyte to be purified, starting an anti-corrosion pump and related valves, controlling the flow rate to be 50L/min, taking the purified liquid for detection, merging the purified liquid into a lead electrolyte circulating system after the purified liquid meets the requirement, and repeatedly purifying unqualified purified liquid until the purified liquid is qualified; secondly, the active carbon exchange column group needs to be desorbed and regenerated after running for about three months. During desorption operation, adding calcium chloride liquid into a desorption agent box, controlling 6-10g/L of calcium chloride, starting an anticorrosive pump and a related valve for desorption, adding pure water into the desorption agent box to wash the exchange column for three times after desorption is completed, and then, carrying out purification operation after washing is completed; then, the desorption solution and the washing solution are pumped to a wet workshop for neutralization and precipitation, valuable elements in the solution are recovered, and the waste solution is sent to a sewage station for disposal.
The above description is only for the preferred embodiment of the present invention, but the scope of the present invention is not limited thereto, and any person skilled in the art should be considered to be within the technical scope of the present invention, and the technical solutions and the inventive concepts thereof according to the present invention should be equivalent or changed within the scope of the present invention.

Claims (7)

1. The method for purifying the lead electrolyte by using the columnar activated carbon comprises the following steps:
s1, lead electrolyte purification: opening a liquid storage tank valve of lead electrolyte to be purified, starting an anti-corrosion pump and related valves, controlling the flow rate to be 50L/min, enabling the lead electrolyte to be purified to enter an activated carbon exchange column group, sampling and analyzing harmful impurities such as bismuth, antimony and the like in the lead electrolyte to be purified after the lead electrolyte to be purified completely passes through the activated carbon exchange column group, taking purified liquid for detection, merging the purified liquid into a lead electrolyte circulating system after the purified liquid meets the requirements, and repeatedly purifying unqualified purified liquid until the purified liquid is qualified;
s2, desorption and regeneration of the activated carbon exchange column group: the active carbon exchange column group is required to be desorbed and regenerated after running for about three months; during desorption operation, lead electrolyte containing harmful impurities such as bismuth, antimony and the like to be purified passes through a columnar active carbon exchange column group to adsorb harmful impurity ions in the lead electrolyte to be purified, calcium chloride liquid is added into a desorption agent box, 6-10g/L of calcium chloride is controlled, an anticorrosion pump and a relevant valve are opened to carry out desorption, pure water is added into the desorption agent box to wash the exchange column for three times after desorption is completed, and purification operation can be carried out after washing is completed;
s3, neutralizing and recycling wastewater: and pumping the desorption solution and the washing solution to a wet workshop for neutralization and precipitation, recovering valuable elements in the solution, and delivering the waste solution to a sewage station for disposal.
2. The method for purifying lead electrolyte using columnar activated carbon as claimed in claim 1, wherein: in S1 and lead electrolyte purification, the active carbon exchange column group is composed of three active carbon exchange columns which are connected in series, the active carbon exchange columns are made of organic glass, and the height-diameter ratio is 5: 1.
3. the method for purifying lead electrolyte using columnar activated carbon as claimed in claim 2, wherein: the exchange column is connected by transparent high-pressure plastic hose, and the hose diameter is 50mm, and pumping power is anticorrosive pump, and the power of pump motor is 5.5 KW.
4. The method for purifying lead electrolyte using columnar activated carbon as claimed in claim 1, wherein: the active carbon in the active carbon exchange column group is columnar coconut shell active carbon.
5. The method for purifying lead electrolyte using columnar activated carbon as claimed in claim 1, wherein: in the step S1 and the lead electrolyte purification, the purification mode is a dynamic mode.
6. The method for purifying lead electrolyte using columnar activated carbon as claimed in claim 1, wherein: the dynamic mode is that the lead electrolyte to be purified is pumped into the active carbon exchange column group by an anticorrosive pump, the flow rate is controlled to be 50L/min, the lead electrolyte to be purified completely passes through the active carbon exchange column group, then the sample is taken to analyze harmful impurities such as bismuth, antimony and the like in the lead electrolyte, and the lead electrolyte can be merged into a lead electrolyte circulating system after being qualified.
7. The method for purifying lead electrolyte using columnar activated carbon as claimed in claim 1, wherein: and in the step S2 and the desorption and regeneration of the activated carbon exchange column group, the activated carbon desorption and regeneration system shares the anticorrosion pump, and the desorption agent is filled in a desorption agent box which is specially manufactured and is connected with the outlet pipe diameter of the anticorrosion pump through a tee joint and a valve.
CN202010817378.6A 2020-08-13 2020-08-13 Method for purifying lead electrolyte by using columnar activated carbon Pending CN112403028A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202010817378.6A CN112403028A (en) 2020-08-13 2020-08-13 Method for purifying lead electrolyte by using columnar activated carbon

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202010817378.6A CN112403028A (en) 2020-08-13 2020-08-13 Method for purifying lead electrolyte by using columnar activated carbon

Publications (1)

Publication Number Publication Date
CN112403028A true CN112403028A (en) 2021-02-26

Family

ID=74853983

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202010817378.6A Pending CN112403028A (en) 2020-08-13 2020-08-13 Method for purifying lead electrolyte by using columnar activated carbon

Country Status (1)

Country Link
CN (1) CN112403028A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114045530A (en) * 2021-11-30 2022-02-15 广东先导稀材股份有限公司 Method for purifying and removing tin from indium sulfate electrolyte

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1091479A (en) * 1993-02-25 1994-08-31 北京有色金属研究总院 A kind of processing method of clarifying lead electrolytic solution
EP2532760A1 (en) * 2011-06-06 2012-12-12 Atotech Deutschland GmbH Device and method for recovering nickel from a nickel plating bath fluid
CN105858779A (en) * 2016-04-15 2016-08-17 江南大学 Method for recycling metal from low-concentration heavy metal ion wastewater
CN108339520A (en) * 2018-04-10 2018-07-31 黄山学院 A kind of depth goes nano-sized iron oxide-charcoal complex, preparation method and its application method of heavy metal in water removal
CN111151221A (en) * 2020-01-13 2020-05-15 黄山学院 Macroporous biochar-based hybrid material for ultra-fast removal of heavy metals in water body and preparation method and application thereof

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1091479A (en) * 1993-02-25 1994-08-31 北京有色金属研究总院 A kind of processing method of clarifying lead electrolytic solution
EP2532760A1 (en) * 2011-06-06 2012-12-12 Atotech Deutschland GmbH Device and method for recovering nickel from a nickel plating bath fluid
CN105858779A (en) * 2016-04-15 2016-08-17 江南大学 Method for recycling metal from low-concentration heavy metal ion wastewater
CN108339520A (en) * 2018-04-10 2018-07-31 黄山学院 A kind of depth goes nano-sized iron oxide-charcoal complex, preparation method and its application method of heavy metal in water removal
CN111151221A (en) * 2020-01-13 2020-05-15 黄山学院 Macroporous biochar-based hybrid material for ultra-fast removal of heavy metals in water body and preparation method and application thereof

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114045530A (en) * 2021-11-30 2022-02-15 广东先导稀材股份有限公司 Method for purifying and removing tin from indium sulfate electrolyte

Similar Documents

Publication Publication Date Title
CN105439355A (en) Polluted acid resource recovery and advanced treatment method and device
CN106587472B (en) A kind of recycling recoverying and utilizing method of the electroplating wastewater containing palladium
CN102491477B (en) Method for removing mercury from high concentration acid
CN105174556A (en) High-acidity high-iron heavy metal wastewater quality-divided resource recycling method
CN109626672A (en) Based on nitrate nitrogen method in electrochemistry and resin combination technique advanced treatment of waste water
CN103991924A (en) Regeneration method of ion exchange resin for processing terminal wastewater of electrolytic manganese production process
CN105238933A (en) Method for removing and recycling mercury element from sulfur dioxide containing smoke
CN203715400U (en) Low-concentration lead-containing wastewater treatment equipment
CN112403028A (en) Method for purifying lead electrolyte by using columnar activated carbon
CN204752826U (en) Resin electrolysis integration gold, palladium recovery system
CN113896361A (en) Method for cleaning and disposing stainless steel pickling acid waste liquid and recycling resources
CN101618898A (en) Method for recovering gold, platinum and porpezite from acidic waste water by ion exchange
CN111762927A (en) Method and device for joint demercuration of high-acidity chemical mercury-containing waste acid liquid
CN113401995A (en) Method for treating and recycling heavy metal contaminated soil leaching waste liquid
CN108483574A (en) A kind of electroplating waste processing equipment and method reducing the useless danger yield of sludge
CN105441685B (en) The method of valuable metal recovery in the high acid waste liquid that a kind of copper anode mud processing procedure is produced
KR102130071B1 (en) Method for simultaneous removal of ammonia, hydrogen sulfide and heavy metal in wastewater
CN103343226A (en) Method and system for recycling zinc from low-concentration zinc containing solution
JP2013119487A (en) Method for treating hydrosilicofluoric acid-containing liquid
CN213924392U (en) Recovery processing device of nickeliferous waste liquid
CN114380361B (en) Method for recycling uranium in uranium-containing wastewater and groundwater through electrochemical reduction enrichment in coexistence of nitrate
CN115465979A (en) Rotational flow electrolysis-ion exchange coupling system and method for deeply removing and recovering heavy metal ions in water body
CN212127781U (en) Nickel recovery device for waste battery wastewater
CN104108818A (en) Heavy metal-containing wastewater treatment method by virtue of ion exchange and cyclone electrolysis technologies
CN201458853U (en) Device for reusing and recovering cyanide rinsing water

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
RJ01 Rejection of invention patent application after publication

Application publication date: 20210226

RJ01 Rejection of invention patent application after publication