CN109013692A - Method for strengthening remediation of heavy metal contaminated soil and application - Google Patents

Method for strengthening remediation of heavy metal contaminated soil and application Download PDF

Info

Publication number
CN109013692A
CN109013692A CN201810957142.5A CN201810957142A CN109013692A CN 109013692 A CN109013692 A CN 109013692A CN 201810957142 A CN201810957142 A CN 201810957142A CN 109013692 A CN109013692 A CN 109013692A
Authority
CN
China
Prior art keywords
electrode
soil
heavy metal
strengthening
anode
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
CN201810957142.5A
Other languages
Chinese (zh)
Inventor
蔡宗平
黄伟良
孙水裕
姚卫康
梁冠杰
李伟新
成景特
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.)
Guangdong Institute Of Mineral Application
Guangdong University of Technology
Guangdong Vocational College of Environmental Protection Engineering
Original Assignee
Guangdong Institute Of Mineral Application
Guangdong University of Technology
Guangdong Vocational College of Environmental Protection Engineering
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 Guangdong Institute Of Mineral Application, Guangdong University of Technology, Guangdong Vocational College of Environmental Protection Engineering filed Critical Guangdong Institute Of Mineral Application
Priority to CN201810957142.5A priority Critical patent/CN109013692A/en
Publication of CN109013692A publication Critical patent/CN109013692A/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C1/00Reclamation of contaminated soil
    • B09C1/08Reclamation of contaminated soil chemically
    • B09C1/085Reclamation of contaminated soil chemically electrochemically, e.g. by electrokinetics

Abstract

The invention provides a method for strengthening remediation of heavy metal contaminated soil and application thereof, and relates to the technical field of soil remediation. A method for strengthening and repairing heavy metal contaminated soil comprises the following steps: and (3) adopting a method of fixing the cathode and gradually shortening the distance between the anode and the cathode to carry out electric remediation on the polluted soil. The repairing method is simple and convenient to operate, strong in controllability, capable of increasing the mobility of heavy metals and the removal rate, remarkable in effect, low in energy consumption and good in application prospect.

Description

A kind of method and application for strengthening restoration of soil polluted by heavy metal
Technical field
The present invention relates to technical field of soil remediation, and in particular to a kind of method for strengthening restoration of soil polluted by heavy metal And application.
Background technique
Technology of Electrodynamics Renovation is one of recovery technique of soil pollution, be it is a kind of green, cleaning, efficiently to pollution The technology that soil environment is handled is to apply DC power supply at contaminated soil both ends, under DC electric field effect, is moved using electricity The removal pollutants such as heavy metal in soil and organic matter such as shifting, electrodialysis and electrophoresis.This method is suitable for in-situ immobilization, without digging Digging body saves expense;Depth is handled simultaneously up to 10-20 meters etc., and treatment effeciency is high;With Environmental compatibility, and it is suitable for Handle heavy metal and organic pollutant etc..Electro reclamation can overcome many defects of previous recovery technique, such as can handle low Infiltrative soil is suitable for multiphase nonuniform soil medium and bulky grain and little particle soil media, can effectively remove soil Middle heavy metal, overall expenses are low etc..Therefore, it has been applied to the reparation of heavy-metal contaminated soil.
However, there is also some problems, such as heavy metal ion to be known as " focusing effect in the deposited phenomenon that cathode generates for the technology Answer ", this is the major obstacle for influencing heavy-metal contaminated soil electro reclamation.Many researchs have such as added strong complexing agent and have waited until soil With use amberplex control pH value and eletrokinetic potential.These improved technical operations are complicated, because introducing additionally The use of chemical substance or equipment leads to secondary pollution.Therefore it finds a kind of effective method and does not add reagent and accelerate to repair Rate becomes urgent problem to be solved.
Summary of the invention
The purpose of the present invention is to provide a kind of methods for strengthening restoration of soil polluted by heavy metal, and this method is easy to operate, Remediation efficiency is improved, soil remediation effect is enhanced, reduces energy consumption.
The present invention solves its technical problem and adopts the following technical solutions to realize.
The present invention proposes a kind of method for strengthening restoration of soil polluted by heavy metal, comprising:
Using fixed negative pole, the method that the distance between anode and cathode is gradually shortened repairs contaminated soil.
The beneficial effects of the present invention are:
The present invention uses fixed negative pole method, and the distance between anode and cathode is gradually shortened, repairs to contaminated soil It is multiple.It is equipped with multiple anodes between the anode and cathode at both ends, successively switches anode after repairing a period of time, realizes that anode approaches Cathode.When starting to repair, the H of anode generation+It is freely accessible to soil, the OH that cathode generates-Since the second filter layer cannot be introduced into soil Earth causes soil pH value to reduce.H+The reverse electromigration of plasma increases the solubility of the heavy metal elements such as Zn, increases and moves Shifting rate finally increases removal rate to accelerate it from the desorption process in soil matrix.Due between cathode anode away from From being gradually shortened, energy is no longer consumed in the part soil for repairing completion, energy consumption needed for reaching same repairing effect also because This and reduce.The restorative procedure is easy to operate, and controllability is strong, significant effect, has biggish superiority, has good application Prospect.
Detailed description of the invention
In order to illustrate the technical solution of the embodiments of the present invention more clearly, below will be to needed in the embodiment attached Figure is briefly described, it should be understood that the following drawings illustrates only certain embodiments of the present invention, therefore is not construed as pair The restriction of range for those of ordinary skill in the art without creative efforts, can also be according to this A little attached drawings obtain other relevant attached drawings.
Fig. 1 is the structural schematic diagram that slot is repaired in electrolysis provided in an embodiment of the present invention.
Specific embodiment
It in order to make the object, technical scheme and advantages of the embodiment of the invention clearer, below will be in the embodiment of the present invention Technical solution be clearly and completely described.The person that is not specified actual conditions in embodiment, according to normal conditions or manufacturer builds The condition of view carries out.Reagents or instruments used without specified manufacturer is the conventional production that can be obtained by commercially available purchase Product.
The method to a kind of reinforcing restoration of soil polluted by heavy metal of the embodiment of the present invention and application carry out specifically below It is bright.
A kind of method for strengthening restoration of soil polluted by heavy metal provided in an embodiment of the present invention, comprising: fixed negative pole is used, The method that the distance between anode and cathode is gradually shortened, repairs contaminated soil.
The basic principle of electrodynamics method is to be inserted into electrode in contaminated soil region, forms electric field after applying direct current, soil Pollutant in the earth directional migration under DC electric field effect is enriched in electrode zone, then passes through other methods removal.Through inventing The lot of experiments of people is found, shortens the distance between positive and negative anodes, fixed negative pole in repair process orderly switches anode array Constantly to approach cathode, the purpose of enhancing repairing polluted soil effect can achieve.Contaminated soil can be containing zinc, iron, copper, The soil of the heavy metal pollutions such as cadmium, lead.
The present invention repairs slot using electrolysis and carries out soil remediation.Specifically, it includes groove body that slot is repaired in electrolysis, it is equipped in groove body First filter layer, the second filter layer and electrode.
Electrode includes first electrode, second electrode and at least one third electrode, and first electrode and second electrode are solid respectively Due to the opposite both ends of groove body, third electrode is set between first electrode and second electrode.First filter layer and the second filtering Groove body is separated to form the first electrolytic cell, soil chamber and the second electrolytic cell by layer, and soil chamber is located at the first electrolytic cell and the second electrolysis Between slot;Soil chamber is used to accommodating electrolysis for holding contaminated soil in the first electrolytic cell, soil chamber and the second electrolytic cell Liquid.In the present embodiment, the first filter layer and the second filter layer are filter paper.First electrode is set in the first electrolytic cell, and second Electrode is set in the second electrolytic cell, and third electrode is set in soil chamber.Generally third electrode is multiple, such as three, five. The embodiment of the present invention uses size for 26cm × 10cm × 10cm groove body, and multiple third electrode spaced sets are in first Between electrode and second electrode.
Electrode is selected from graphite electrode, titanium alloy electrode and stainless steel electrode, and the shape of electrode is plate or rodlike or net Shape.
There is power supply anode and cathode, second electrode to be electrically connected with cathode, the input terminal of single pole multiple throw and power supply Anode electrical connection, first electrode, third electrode are electrically connected with the output end of single pole multiple throw respectively, pass through single pole multiple throw Realize the variation of anode.Processor is electrically connected with single pole multiple throw, for controlling first electrode or a third electrode and electricity The anode electrical connection in source.Timer is equipped in processor, for controlling first electrode or a third electrode according to preset time It is electrically connected with the anode of power supply.
Soil and electrolyte are placed in groove body, when starting to repair, first electrode is electrically connected with the anode of power supply, and second Electrode is electrically connected with cathode, carries out electro reclamation.After repairing preset time, the connection of first electrode and anode is disconnected, along from the Third electrode is successively electrically connected with the anode of power supply to the direction of second electrode, third electrode is electrically connected with anode by one electrode It connects, and is disconnected again after repairing preset time, realize that anode approaches cathode.With the contracting of distance between third electrode and second electrode Short, preset repair time gradually extends, and such as initially repair time is 5h every time, and last 2 repair time is 10h.Groove body Equipped with pump, circular electrolyte avoids generating concentration gradient.
Further, electrolyte is the organic monoacid aqueous solution that concentration is 0.01~0.2mol/L.Organic monoacid is selected from cream At least one of acid, citric acid and acetic acid.
Further, the volume ratio of soil and electrolyte is 1:1~3.
Further, in repair process, the intracorporal electric field strength of slot is 1~5V/cm, and electric field strength is constant.
When starting to repair, the H of anode generation+It is freely accessible to soil, the OH that cathode generates-Since the second filter layer can not be into Enter soil, soil pH value is caused to reduce.H+The reverse electromigration of plasma increases the solubility of the heavy metal elements such as Zn, increases Mobility to accelerate it from the desorption process in soil matrix finally increases removal rate.This is because approaching electrode During method is repaired, balanced balanced current is larger, promotes H+Generation, at the same time, cathode is constantly approached to anode, this makes H+It more concentrates between the two poles of the earth, to reduce the pH value of two interpolar soil.According to experimental design, two interelectrode ranges are Effective operation interval of electrode method reparation is approached, the reduction of two interpolar soil pH values means that the H+ of generation by more effective land productivity It uses, this would be even more beneficial to the release of Zn in soil.
Less, current potential is higher, is conducive to heavy metal ion for the oxidation-reduction potential variation of this method treated soil Migration.Lower pH value and higher oxidation-reduction potential are all conducive to release heavy metal from soil particle and accelerate electric power Learn rehabilitating soil process.
Since the distance between cathode anode is gradually shortened, energy is no longer consumed in the part soil for repairing completion, to be reached It is also therefore reduced to energy consumption needed for same repairing effect.This method is easy to operate, improves remediation efficiency, enhances soil remediation Effect reduces energy consumption, can be applied to field of environmental pollution control.
Feature and performance of the invention are described in further detail with reference to embodiments.
Embodiment 1
Present embodiments provide a kind of method for strengthening restoration of soil polluted by heavy metal:
It will be put into groove body in weakly alkaline sandy soil, the lactic acid solution that concentration is 0.1mol/L is added.Soil and electrolysis The volume ratio of liquid is 1:2.5.Soil in the present embodiment contains heavy metal zinc, and Zn content reaches 265mgkg-1, moisture content is 9.1%, starting pH is 7.6.
It is equipped with 5 third electrodes in groove body, is equidistantly arranged successively along the direction of first electrode to second electrode.By first Electrode is electrically connected with the anode of power supply, and second electrode is electrically connected with cathode, carries out electro reclamation.The intracorporal electric field strength of slot is 5V/cm。
After repairing 5h, the anode of first electrode and power supply is disconnected, it will be near the third electrode of first electrode and power supply Anode electrical connection, carries out electro reclamation.Then after being spaced 5h, the third electrode is disconnected, by second third electrode and power supply Anode electrical connection, carries out electro reclamation.After being so switched to the 4th third electrode, electro reclamation 10h, then disconnect, connection the Five third electrodes and anode, repair 10h.
Embodiment 2
Present embodiments provide a kind of method for strengthening restoration of soil polluted by heavy metal:
It will be put into groove body in weakly alkaline sandy soil, the solution that concentration is 0.01mol/L is added.Soil and electrolyte Volume ratio is 1:1.Soil in the present embodiment contains heavy metal zinc, and Zn content reaches 265mgkg-1, moisture content 9.1%, Originating pH is 7.6.
It is equipped with 5 third electrodes in groove body, is equidistantly arranged successively along the direction of first electrode to second electrode.By first Electrode is electrically connected with the anode of power supply, and second electrode is electrically connected with cathode, carries out electro reclamation.The intracorporal electric field strength of slot is 1V/cm。
After repairing 5h, the anode of first electrode and power supply is disconnected, it will be near the third electrode of first electrode and power supply Anode electrical connection, carries out electro reclamation.Then after being spaced 5h, the third electrode is disconnected, by second third electrode and power supply Anode electrical connection, carries out electro reclamation.Such one until the 5th third electrode.
Embodiment 3
Present embodiments provide a kind of method for strengthening restoration of soil polluted by heavy metal:
It will be put into groove body in weakly alkaline sandy soil, the citric acid solution that concentration is 0.2mol/L is added.Soil and electricity The volume ratio for solving liquid is 1:3.Soil in the present embodiment contains heavy metal zinc, and Zn content reaches 265mgkg-1, moisture content is 9.1%, starting pH is 7.6.
It is equipped with 3 third electrodes in groove body, is equidistantly arranged successively along the direction of first electrode to second electrode.By first Electrode is electrically connected with the anode of power supply, and second electrode is electrically connected with cathode, carries out electro reclamation.The intracorporal electric field strength of slot is 3V/cm。
After repairing 5h, the anode of first electrode and power supply is disconnected, it will be near the third electrode of first electrode and power supply Anode electrical connection, carries out electro reclamation.Then after being spaced 5h, the third electrode is disconnected, by second third electrode and power supply Anode electrical connection, carries out electro reclamation.After being so switched to third third electrode, electro reclamation 10h.
Embodiment 4
Present embodiments provide a kind of method for strengthening restoration of soil polluted by heavy metal:
It will be put into groove body in weakly alkaline sandy soil, the acetic acid solution that concentration is 0.05mol/L is added.Soil and electrolysis The volume ratio of liquid is 1:2.Soil in the present embodiment contains heavy metal zinc, and Zn content reaches 265mgkg-1, moisture content is 9.1%, starting pH is 7.6.
It is equipped with 5 third electrodes in groove body, is equidistantly arranged successively along the direction of first electrode to second electrode.By first Electrode is electrically connected with the anode of power supply, and second electrode is electrically connected with cathode, carries out electro reclamation.The intracorporal electric field strength of slot is 2V/cm。
After repairing 5h, the anode of first electrode and power supply is disconnected, it will be near the third electrode of first electrode and power supply Anode electrical connection, carries out electro reclamation.Then after being spaced 5h, the third electrode is disconnected, by second third electrode and power supply Anode electrical connection, carries out electro reclamation.After being so switched to the 4th third electrode, electro reclamation 10h, then disconnect, connection the Five third electrodes and anode, repair 10h.
Embodiment 5
Present embodiments provide a kind of method for strengthening restoration of soil polluted by heavy metal:
It will be put into groove body in weakly alkaline sandy soil, the lactic acid solution that concentration is 0.1mol/L is added.Soil and electrolysis The volume ratio of liquid is 1:2.Soil in the present embodiment contains heavy metal zinc, and Zn content reaches 265mgkg-1, moisture content is 9.1%, starting pH is 7.6.
It is equipped with 8 third electrodes in groove body, is equidistantly arranged successively along the direction of first electrode to second electrode.By first Electrode is electrically connected with the anode of power supply, and second electrode is electrically connected with cathode, carries out electro reclamation.The intracorporal electric field strength of slot is 5V/cm。
After repairing 5h, the anode of first electrode and power supply is disconnected, it will be near the third electrode of first electrode and power supply Anode electrical connection, carries out electro reclamation.Then after being spaced 5h, the third electrode is disconnected, by second third electrode and power supply Anode electrical connection, carries out electro reclamation.After being so switched to the 5th third electrode, electro reclamation 10h, then disconnect, successively connect The the 6th, the 7th third electrode and anode are connect, 10h is repaired.
Comparative example 1
This comparative example provides the method repairing polluted soil using fixed electrode, is with the difference place of embodiment 1, It is not provided with third electrode, during electro reclamation, first electrode is electrically connected with the anode of power supply always.Soil in the present embodiment Earth contains heavy metal zinc, and Zn content reaches 265mgkg-1, moisture content 9.1%, starting pH is 7.6.
Test example
Repair the measurement of front and back pedotheque content of beary metal: Soil Heavy Metal Elements Content measurement uses HCl-HNO3- HF-HClO4Method digestion, thoroughly destroys the mineral lattice of soil, fully enters the element to be measured in sample in test solution.Pass through The value of measurement calculates the removal efficiency of zinc.
PH value and conductance measurement: using Tu Shui than 1: 2.5 ultrasonic vibration 15min, 30min is stood.It should need in the process Pay attention to avoiding that there is volatile acid or ammonium hydroxide in air.Then combination electrode is inserted into the dirty solution of lower part, and is gently agitated for, Lower pH value is counted after equal pH instrument stable reading.Pedotheque takes with pH measurement unanimously in the measurement of soil conductivity.Soil is Soil after reparation.The result is as follows:
1 test result of table
Zinc removal efficiency/% PH value
Embodiment 1 63 5
Embodiment 2 62 5.5
Embodiment 3 61 5.5
Embodiment 4 63 5
Embodiment 5 64 5
Comparative example 1 37 6
As shown in Table 1, Examples 1 to 5 is compared with comparative example 1, and the pH value of the soil of embodiment is relatively low, explanation H in soil+It is more effectively used, is more advantageous to the release of Zn in soil, help to increase removal rate.Embodiment 1 The removal efficiency of~5 zinc is all larger than the removal efficiency of the zinc of comparative example 1, illustrates soil remediation method effect provided by the invention Significantly, remediation efficiency can be effectively improved.
Embodiments described above is a part of the embodiment of the present invention, instead of all the embodiments.Reality of the invention The detailed description for applying example is not intended to limit the range of claimed invention, but is merely representative of selected implementation of the invention Example.Based on the embodiments of the present invention, obtained by those of ordinary skill in the art without making creative efforts Every other embodiment, shall fall within the protection scope of the present invention.

Claims (10)

1. a kind of method for strengthening restoration of soil polluted by heavy metal characterized by comprising
Using fixed negative pole, the method that the distance between anode and cathode is gradually shortened carries out electro reclamation to contaminated soil.
2. the method according to claim 1 for strengthening restoration of soil polluted by heavy metal, which is characterized in that repaired using electrolysis Slot carries out soil remediation;
It includes groove body, electrode and power supply that slot is repaired in the electrolysis;
The electrode includes first electrode, second electrode and at least one third electrode, the first electrode and second electricity Pole is individually fixed in the opposite both ends of the groove body, the third electrode be set to the first electrode and the second electrode it Between;
The power supply has anode and cathode;
Soil and electrolyte are placed in the groove body, the first electrode is electrically connected with the anode, the second electrode It is electrically connected with the cathode, carries out electro reclamation;
After repairing preset time, the connection of the first electrode Yu the anode is disconnected, third electrode and the anode are electrically connected It connects, then is repaired.
3. the method according to claim 2 for strengthening restoration of soil polluted by heavy metal, which is characterized in that the electrode includes Multiple third electrodes, multiple third electrode spaced sets are between the first electrode and the second electrode.
4. the method according to claim 3 for strengthening restoration of soil polluted by heavy metal, which is characterized in that disconnect described first After the connection of electrode and the anode, edge is from the first electrode to the direction of the second electrode successively by third electrode and institute Positive electrical connection is stated, and is disconnected again after repairing the preset time.
5. the method according to claim 2 for strengthening restoration of soil polluted by heavy metal, which is characterized in that the electrolyte is Concentration is the environment amenable organic monoacid aqueous solution of 0.01~0.2mol/L.
6. the method according to claim 5 for strengthening restoration of soil polluted by heavy metal, which is characterized in that the organic monoacid Selected from least one of lactic acid, citric acid and acetic acid.
7. the method according to claim 2 for strengthening restoration of soil polluted by heavy metal, which is characterized in that the soil and institute The volume ratio for stating electrolyte is 1:1~3.
8. the method according to claim 2 for strengthening restoration of soil polluted by heavy metal, which is characterized in that in repair process, The intracorporal electric field strength of slot is 1~5V/cm.
9. the method according to claim 2 for strengthening restoration of soil polluted by heavy metal, which is characterized in that the shape of the electrode Shape is respectively any one of plate, rodlike, netted.
10. the method as described in any one of claim 1 to 9 for strengthening restoration of soil polluted by heavy metal is in the side of curbing environmental pollution The application in face.
CN201810957142.5A 2018-08-21 2018-08-21 Method for strengthening remediation of heavy metal contaminated soil and application Pending CN109013692A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810957142.5A CN109013692A (en) 2018-08-21 2018-08-21 Method for strengthening remediation of heavy metal contaminated soil and application

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810957142.5A CN109013692A (en) 2018-08-21 2018-08-21 Method for strengthening remediation of heavy metal contaminated soil and application

Publications (1)

Publication Number Publication Date
CN109013692A true CN109013692A (en) 2018-12-18

Family

ID=64627500

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810957142.5A Pending CN109013692A (en) 2018-08-21 2018-08-21 Method for strengthening remediation of heavy metal contaminated soil and application

Country Status (1)

Country Link
CN (1) CN109013692A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113118201A (en) * 2021-04-06 2021-07-16 沈阳大学 Electric synergic remediation method for heavy metal-organic compound contaminated soil based on compressed electric field
CN114472496A (en) * 2022-01-26 2022-05-13 中国葛洲坝集团生态环境工程有限公司 Pretreatment system for reducing water content and heavy metal content of polluted soil
CN116603852A (en) * 2023-06-15 2023-08-18 江苏暨之阳环保科技有限公司 Electrocatalytic spray repair process and equipment for heavy metal contaminated soil

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104226677A (en) * 2014-09-05 2014-12-24 华北电力大学 Device and method for restoring phenanthrene contaminated soil by using two-way approaching method in combined with solubilizer
CN206316141U (en) * 2016-12-08 2017-07-11 中建中环工程有限公司 A kind of processing unit of electro reclamation heavy-metal contaminated soil

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104226677A (en) * 2014-09-05 2014-12-24 华北电力大学 Device and method for restoring phenanthrene contaminated soil by using two-way approaching method in combined with solubilizer
CN206316141U (en) * 2016-12-08 2017-07-11 中建中环工程有限公司 A kind of processing unit of electro reclamation heavy-metal contaminated soil

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
GANG LI 等: "Comparison of approaching and fixed anodes for avoiding the ‘focusing’ effect during electrokinetic remediation of chromium-contaminated soil", 《CHEMICAL ENGINEERING JOURNAL》 *
LJILJANA RAJIĆ 等: "Enhancing electrokinetic lead removal from sediment: Utilizing the moving anode technique and increasing the cathode compartment length", 《ELECTROCHIMICA ACTA》 *
郑燊燊等: "电动修复Cd污染土壤的DBLM模型", 《农业环境科学学报》 *
郑燊燊等: "逼近阳极法电动力学修复重金属污染土壤", 《农业环境科学学报》 *

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113118201A (en) * 2021-04-06 2021-07-16 沈阳大学 Electric synergic remediation method for heavy metal-organic compound contaminated soil based on compressed electric field
CN114472496A (en) * 2022-01-26 2022-05-13 中国葛洲坝集团生态环境工程有限公司 Pretreatment system for reducing water content and heavy metal content of polluted soil
CN114472496B (en) * 2022-01-26 2023-07-14 葛洲坝集团生态环保有限公司 Pretreatment system for reducing water content and heavy metal content of polluted soil
CN116603852A (en) * 2023-06-15 2023-08-18 江苏暨之阳环保科技有限公司 Electrocatalytic spray repair process and equipment for heavy metal contaminated soil
CN116603852B (en) * 2023-06-15 2023-11-03 江苏暨之阳环保科技有限公司 Electrocatalytic spray repair process and equipment for heavy metal contaminated soil

Similar Documents

Publication Publication Date Title
CN202356398U (en) Electric repairing device for removing heavy metals and organic pollutants in soil
CN109013692A (en) Method for strengthening remediation of heavy metal contaminated soil and application
CN102513348A (en) Electric complex-strengthening repairing method and device of heavy metal-organic co-contaminated soil
CN104368596A (en) In-situ treatment method for electrically repairing heavy metal contaminated soil based on plastic electrode
CN104909526B (en) Device for removing heavy metals in sludge by using electro-dynamic method and synchronously and deeply dehydrating sludge
CN203304274U (en) Device for intensively treating heavy metal contaminated soil by power-driven method
CN101781001A (en) Method for processing effluent by two-stage electrolysis and device thereof
CN204338567U (en) Based on the electric osmose system of the electro reclamation heavy-metal contaminated soil of plastic electrode
CN207325582U (en) A kind of electric power soil repair system based on solar energy
CN104384179A (en) In-situ restoration apparatus for heavy metal pollutants in soil and restoration method thereof
CN103736718A (en) Electrokinetic remediation method and device of heavy metal contaminated soil
CN109513741A (en) Device and restorative procedure for repairing polluted soil
CN109719122A (en) The processing method and processing device of heavy metal ion in a kind of removal soil (water body) with adsorbent
CN206316141U (en) A kind of processing unit of electro reclamation heavy-metal contaminated soil
CN106904799B (en) Electric repair strengthening device and method for removing heavy metals in sludge by using same
CN106424117A (en) Device for electro-kinetic remediation of heavy metal contaminated soil by utilizing copper salt reinforced cathode
CN110947751B (en) Device and method for restoring cadmium-polluted soil through electric auxiliary leaching
CN106430746A (en) Process for pretreating natural gas produced water with electric flocculation
CN105642664B (en) A kind of reinforced electric power original position soil prosthetic device and method
CN103302091B (en) Sequencing-batch polluted soil remediation method and device
CN206779150U (en) A kind of electrolytic cell of interchangeable electrode
CN109047321A (en) A kind of multi-electrode system electro reclamation soil method based on polyaniline auxiliary electrode
CN204173965U (en) For removing organic photo electrocatalysis reactor in sewage
CN113264617A (en) Dielectrophoresis-assisted radioactive marine sewage microalgae cleaning device and method
CN207188449U (en) The electro reclamation device of heavy-metal contaminated soil

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: 20181218

RJ01 Rejection of invention patent application after publication