CN101138767A - Method for renovating soil polluted by heavy metal - Google Patents

Method for renovating soil polluted by heavy metal Download PDF

Info

Publication number
CN101138767A
CN101138767A CNA2007100534259A CN200710053425A CN101138767A CN 101138767 A CN101138767 A CN 101138767A CN A2007100534259 A CNA2007100534259 A CN A2007100534259A CN 200710053425 A CN200710053425 A CN 200710053425A CN 101138767 A CN101138767 A CN 101138767A
Authority
CN
China
Prior art keywords
electrode
soil
negative
acid
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
CNA2007100534259A
Other languages
Chinese (zh)
Inventor
袁松虎
陆晓华
李泰平
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.)
Huazhong University of Science and Technology
Original Assignee
Huazhong University of Science and Technology
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 Huazhong University of Science and Technology filed Critical Huazhong University of Science and Technology
Priority to CNA2007100534259A priority Critical patent/CN101138767A/en
Publication of CN101138767A publication Critical patent/CN101138767A/en
Pending legal-status Critical Current

Links

Images

Abstract

The present invention discloses a method of repairing soil polluted by heavy metal. Procedures of repair method are as following: (1) both sides of the soil are provided with electrode wells. Parallel negative electrode and positive electrode are installed in the electrode well, spaced at 0.1 to 1m. When the positive electrode adopts iron or aluminum, the negative electrode adopts manganese dioxide, carbon or copper; when the positive electrode adopts the carbon, the negative electrode adopts manganese dioxide; (2) the electrode well is filled with flushing fluid whose level is higher than that of the soil, thus, making materials of the negative and positive electrodes soaked in the flushing liquid; the flushing liquid is water or acid solution whose concentration is less than 2mol/l; (3) the negative and positive electrodes are connected and conduction time lasts for 30 to 500 days. The present invention makes negative and positive electrodes made up of different materials to have electrode reaction resulting from electrode potential of electrode surface, thus, forming primary batteries to produce potential difference to have pollutants in the soil between the negative and positive electrodes remove. Therefore, requirement for high consumption of additional power can be prevented. The method has advantages of low consumption, environment-friendly, good treatment effect and easy operation.

Description

A kind of restorative procedure of heavy-metal contaminated soil
Technical field
The invention belongs to the soil remediation technical field, be specifically related to a kind of restorative procedure of heavy-metal contaminated soil.
Technical background
Along with the development of industrial and agricultural production, a large amount of heavy metal contaminants enter into environment, and finally are accumulated in the soil, make soil pollution more and more serious.The direct economic loss that the agricultural product that the annual production of China contains heavy metal cause reaches 20,000,000,000 yuan, and problem is very serious.Soil pollution has become one of major obstacles of restriction agricultural products in China international trade and social sustainable development, and contaminated soil is badly in need of repairing.
Present contaminated soil recovery technique mainly comprises soil replacement method, burning method, solvent drip washing, steam extraction, chemical oxidation and biological treatment (comprising plant treatment) etc.Soil replacement method and burning method all have bigger consumption to manpower and materials.Biological treatment requires substance to be processed to have bioavailability preferably, requires to have the bacterial classification of high selectivity.Additive method requires processed soil to have permeability preferably.Electrodynamics soil remediation technology is a kind of method that develops at hyposmosis clayed soil specially, utilizes effects such as electromigration and electrodialysis that pollutant is moved from soil, realizes the reparation of contaminated soil.
Yet, traditional a large amount of electric energy of electrodynamics soil remediation Technology Need consumption, according to external authoritative institution statistics, the direct power consumption of repairing every necromancer earth is about about 100 dollars.In addition, this technology can damage soil when removing pollutant in soil, as makes the soil acidification of anode region and make the alkalization of soils in cathodic region.The factor of this two aspect, particularly high energy consumption has directly limited the actual through engineering approaches of electrodynamics technology and has used.Therefore, reduce the electric energy loss of electrodynamics technology, reduce simultaneously the destruction of handling soil region is necessary.
Summary of the invention
The objective of the invention is to overcome the deficiency of existing electrodynamics soil remediation technology, a kind of restorative procedure of heavy-metal contaminated soil is provided, this method is consumed power not, and is very little to the destruction of soil, has the low and eco-friendly advantage of operating cost.
The restorative procedure of heavy-metal contaminated soil provided by the invention the steps include:
(1) on pending soil both sides electrode wells is set, the yin, yang electrode is installed in the electrode wells, the parallel placement of electrode, electrode spacing is 0.1-1m; When anode material adopted iron or aluminium, negative electrode adopted manganese dioxide, carbon or copper; When anode material adopted carbon, negative electrode adopted manganese dioxide;
(2) in above-mentioned electrode wells, fill flushing liquor, make the liquid level of electrode wells be higher than processing soil height, and the cathode and anode material is immersed in the flushing liquor; Flushing liquor is water or the concentration acid solution smaller or equal to 2mol/L, and acid is sulfuric acid, hydrochloric acid, nitric acid, oxalic acid, ethylenediamine tetra-acetic acid or citric acid;
(3) connect cathode and anode, conduction time is between 30-500 days.
The inventive method uses materials with different properties (as iron and carbon) to serve as anode and cathode, make the electrode reaction that different electrode potentials take place electrode surface constitute galvanic cell, thereby produce the migration that potential difference drives pollutant in soil between anode and cathode, avoided the required high energy consumption of additional power source.This method can also realize the increase of potential difference by the series connection of a plurality of galvanic cells, thereby improves treatment effect.Compare with traditional electrodynamics technology, this galvanic cell soil remediation technology is consumed power not, and is very little to the destruction of soil, has the low and environmental friendliness advantage of operating cost.In a word, the inventive method has advantages such as safe and reliable and easy and simple to handle, has the value of application.
Description of drawings
Fig. 1 is a principle schematic of the present invention.
Fig. 2 is the soil remediation installation drawing of single galvanic cell.
Fig. 3 is the soil remediation installation drawing of a plurality of galvanic cell series connection.
Fig. 4 is the treatment effect of galvanic cell technology to copper polluted soil.
Fig. 5 is the treatment effect of galvanic cell technology to cadmium pollution soil.
The specific embodiment
The electric field that the inventive method produces by galvanic cell drives heavy metal contaminants and moves from soil, reaches the reparation of contaminated soil.As shown in Figure 1, use materials with different properties to serve as anode and cathode on the both sides of contaminated soil, connect anode and cathode with lead and constitute galvanic cell, drive the inorganic ions generation electromigration in the contaminated soil, cation is to cathodic migration, and the anion anode is moved.
Below in conjunction with accompanying drawing the inventive method is further described.
1., the electrode setting: on pending soil both sides electrode wells is set, installing electrodes in the electrode wells, the parallel symmetry of electrode is placed, electrode spacing is 0.1-1m, uses lead that anode and cathode is coupled together, and constitutes a complete galvanic cell, as shown in Figure 2; A plurality of electrode wells perhaps are set, anode and cathode alternately is installed, use lead that the negative electrode of a galvanic cell is continuous with the anode of adjacent galvanic cell, realize the series connection of a plurality of galvanic cells, as shown in Figure 3; Anode is selected reproducibility material preferably for use, and as iron, aluminium, carbon, negative electrode is selected oxidisability material preferably for use, as carbon, manganese dioxide, guarantees that different electrode reactions takes place anode and cathode.
2., flushing liquor setting: the acid solution (sulfuric acid, hydrochloric acid, nitric acid, oxalic acid, ethylenediamine tetra-acetic acid, citric acid) of filling 0-2mol/L in the electrode wells, and by pump with being communicated with towards Xian's liquid storage tank, the liquid level that guarantees electrode wells is higher than processing soil height, and make soil have certain humidity, the cathode and anode material is immersed in the flushing liquor.
3., be communicated with processing: use lead to connect anode and cathode, processing soil is under the weak electric field effect of anode and cathode generation, the electrodynamics migration effect will take place in pollutant wherein, cation anode (negative electrode of galvanic cell) migration, anion is to negative electrode (anode of galvanic cell) migration, and interstitial water generation electrodialysis migration makes pollutant that corresponding migration take place.Be the intensive treatment process, in service can be on soil spray irrigation liquid.Different with concentration according to pollutant kind, generally continued conduction time between 30-500 days.
Embodiment 1: copper is a kind of typical heavy metal contaminants, and environment is had bigger harmfulness.Delivery is intended copper polluted soil 150g, and copper content is 170mg/kg, configuration moisture content 50%, and the galvanic cell reaction unit of packing into is (among the Φ 5cm * 8cm).Anode uses iron filings, and negative electrode uses activated carbon, and the anode chamber and the cathode chamber (100mL) is filled the dilute acid soln (0mol/L, the sulfuric acid of 0.1mol/L and 0.5mol/L) of variable concentrations, is communicated with anode and cathode with lead.Handle after 30 days, find that by analysis copper concentration is raise to carbon gradually by iron, as shown in Figure 4.X/L is a test point apart from ferroelectric pole span from divided by the reactor length overall.
Embodiment 2: cadmium is a kind of typical heavy metal contaminants, and environment is had great harmfulness.Get a certain amount of simulation cadmium pollution soil, cadmium content is 160mg/kg, configuration moisture content 50%, and the galvanic cell reaction unit of packing into (among the Φ 5cm * 20cm), is connected three galvanic cell devices simultaneously by the mode shown in Fig. 2 b.Anode uses iron filings, and negative electrode uses activated carbon, and the anode chamber and the cathode chamber (100mL) is filled the 0.2mol/L hydrochloric acid solution, is communicated with anode and cathode with lead.Handle after 30 days, find that by analysis cadmium concentration is raise to carbon gradually by iron in the single reaction post, the series connection of a plurality of galvanic cell reaction columns can the extension process zone, as shown in Figure 5.X/L is a test point apart from ferroelectric pole span from divided by the reactor length overall, the situation when first, second of C1, C2 and C3 representative series connection and the 3rd galvanic cell, C are represented single galvanic cell.

Claims (1)

1. the restorative procedure of a heavy-metal contaminated soil the steps include:
(1) on pending soil both sides electrode wells is set, the yin, yang electrode is installed in the electrode wells, the parallel placement of electrode, electrode spacing is 0.1-1m; When anode material adopted iron or aluminium, negative electrode adopted manganese dioxide, carbon or copper; When anode material adopted carbon, negative electrode adopted manganese dioxide;
(2) in above-mentioned electrode wells, fill flushing liquor, make the liquid level of electrode wells be higher than processing soil height, and the cathode and anode material is immersed in the flushing liquor; Flushing liquor is water or the concentration acid solution smaller or equal to 2mol/L, and acid is sulfuric acid, hydrochloric acid, nitric acid, oxalic acid, ethylenediamine tetra-acetic acid or citric acid;
(3) use lead to connect cathode and anode, conduction time is between 30-500 days.
CNA2007100534259A 2007-09-29 2007-09-29 Method for renovating soil polluted by heavy metal Pending CN101138767A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CNA2007100534259A CN101138767A (en) 2007-09-29 2007-09-29 Method for renovating soil polluted by heavy metal

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CNA2007100534259A CN101138767A (en) 2007-09-29 2007-09-29 Method for renovating soil polluted by heavy metal

Publications (1)

Publication Number Publication Date
CN101138767A true CN101138767A (en) 2008-03-12

Family

ID=39190967

Family Applications (1)

Application Number Title Priority Date Filing Date
CNA2007100534259A Pending CN101138767A (en) 2007-09-29 2007-09-29 Method for renovating soil polluted by heavy metal

Country Status (1)

Country Link
CN (1) CN101138767A (en)

Cited By (25)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102247980A (en) * 2011-07-04 2011-11-23 中国科学院过程工程研究所 Remediation agent for leaching soil polluted by heavy metal chrome
CN102371267A (en) * 2011-09-04 2012-03-14 常州浩瀚新材料科技有限公司 Technical device for quickly repairing soil pollution by advanced oxidation
CN102728608A (en) * 2012-06-13 2012-10-17 广西来宾市天仁生物有机肥有限责任公司 Leaching device for processing heavy metal in house refuse and sludge by using citric acid
CN103240268A (en) * 2013-05-09 2013-08-14 中国石油大学(华东) Two-dimensional inhomogeneous field experiment device for electrically repairing polluted soil
CN103252342A (en) * 2013-05-10 2013-08-21 华北电力大学 Electrodynamic force ultraviolet photolysis in-situ repair device and repair method thereof
CN103286120A (en) * 2013-06-07 2013-09-11 华北电力大学 Microwave electric soil in-situ restoration device and restoration method
CN103706622A (en) * 2013-12-25 2014-04-09 江苏大地益源环境修复有限公司 Method and device for obtaining uniform electric field for electrically repairing polluted soil
CN103752599A (en) * 2013-12-25 2014-04-30 天津生态城环保有限公司 Equipment and method for restoring heavy metal contaminated soil by combining leaching and electro-deposition
CN104492796A (en) * 2014-12-09 2015-04-08 江苏盖亚环境工程有限公司 Electrokinetic remediation method of heavy metal contaminated soil
CN105642664A (en) * 2016-03-16 2016-06-08 江西省环境保护科学研究院 Enhancement type electrodynamic force in-situ soil remediation device and method
CN106001077A (en) * 2016-07-28 2016-10-12 崔晓辉 Device for restoring soil polluted by heavy metal chromium
CN106269835A (en) * 2016-11-10 2017-01-04 长江水利委员会长江科学院 Heavy metal-polluted soil electricity based on electronic geotextiles promotees drip washing removal device and method
CN106623408A (en) * 2016-12-27 2017-05-10 常州大学 Electrokinetic remediation technology and method for removing heavy metal contaminated soil
CN106881339A (en) * 2017-02-22 2017-06-23 长江水利委员会长江科学院 Pin-connected panel original position drip washing is electronic with EKG to cooperate with the device and method for removing heavy metal-polluted soil
CN108687130A (en) * 2018-06-22 2018-10-23 中节能大地环境修复有限公司 A kind of method of nitrobenzene in oxidation soil
CN108906851A (en) * 2018-07-09 2018-11-30 北京中岩大地科技股份有限公司 A kind of high-moisture low-permeability waste residue removes saline and alkaline dehydration combined governance method
CN108994046A (en) * 2018-07-09 2018-12-14 北京中岩大地科技股份有限公司 A kind of dehydrated in situ of low-permeability high-moisture waste residue removes saline and alkaline method
CN109622597A (en) * 2019-01-24 2019-04-16 天津友爱环保科技有限公司 A kind of electrochemical repair method of heavy-metal contaminated soil
CN109622598A (en) * 2019-01-29 2019-04-16 华中农业大学 A method of based on galvanic principles restoration of soil polluted by heavy metal
CN109772881A (en) * 2019-03-06 2019-05-21 韶关学院 A method of Cd-polluted farmland soil is repaired and efficiently utilized using fragrant plant
CN109848203A (en) * 2019-03-23 2019-06-07 中国农业科学院农田灌溉研究所 A kind of restorative procedure for Cadmium in Soil of degrading
CN110510709A (en) * 2019-08-06 2019-11-29 东华大学 A kind of removable Cd2+Primary battery and its application
CN112692051A (en) * 2021-01-25 2021-04-23 明志科技大学 Method and equipment for removing pollutants by using beneficial microorganism mixed bacterial liquid
CN113385527A (en) * 2021-05-31 2021-09-14 山东大学 Method and device for repairing heavy metal contaminated soil suspension by adopting pulse current
CN116425315A (en) * 2023-05-25 2023-07-14 中交第三公路工程局有限公司 Constructed wetland system based on electrodynamic strengthening denitrification

Cited By (33)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102247980A (en) * 2011-07-04 2011-11-23 中国科学院过程工程研究所 Remediation agent for leaching soil polluted by heavy metal chrome
CN102371267A (en) * 2011-09-04 2012-03-14 常州浩瀚新材料科技有限公司 Technical device for quickly repairing soil pollution by advanced oxidation
CN102371267B (en) * 2011-09-04 2014-07-16 常州浩瀚新材料科技有限公司 Technical device for quickly repairing soil pollution by advanced oxidation
CN102728608A (en) * 2012-06-13 2012-10-17 广西来宾市天仁生物有机肥有限责任公司 Leaching device for processing heavy metal in house refuse and sludge by using citric acid
CN103240268B (en) * 2013-05-09 2014-06-11 中国石油大学(华东) Two-dimensional inhomogeneous field experiment device for electrically repairing polluted soil
CN103240268A (en) * 2013-05-09 2013-08-14 中国石油大学(华东) Two-dimensional inhomogeneous field experiment device for electrically repairing polluted soil
CN103252342A (en) * 2013-05-10 2013-08-21 华北电力大学 Electrodynamic force ultraviolet photolysis in-situ repair device and repair method thereof
CN103252342B (en) * 2013-05-10 2015-04-15 华北电力大学 Electrodynamic force ultraviolet photolysis in-situ repair device and repair method thereof
CN103286120A (en) * 2013-06-07 2013-09-11 华北电力大学 Microwave electric soil in-situ restoration device and restoration method
CN103752599A (en) * 2013-12-25 2014-04-30 天津生态城环保有限公司 Equipment and method for restoring heavy metal contaminated soil by combining leaching and electro-deposition
CN103706622A (en) * 2013-12-25 2014-04-09 江苏大地益源环境修复有限公司 Method and device for obtaining uniform electric field for electrically repairing polluted soil
CN103706622B (en) * 2013-12-25 2015-12-09 江苏大地益源环境修复有限公司 The uniform electric field preparation method of Electrokinetic Remediation of Polluted Soils and device
CN104492796A (en) * 2014-12-09 2015-04-08 江苏盖亚环境工程有限公司 Electrokinetic remediation method of heavy metal contaminated soil
CN105642664A (en) * 2016-03-16 2016-06-08 江西省环境保护科学研究院 Enhancement type electrodynamic force in-situ soil remediation device and method
CN105642664B (en) * 2016-03-16 2019-07-26 江西省环境保护科学研究院 A kind of reinforced electric power original position soil prosthetic device and method
CN106001077A (en) * 2016-07-28 2016-10-12 崔晓辉 Device for restoring soil polluted by heavy metal chromium
CN106269835A (en) * 2016-11-10 2017-01-04 长江水利委员会长江科学院 Heavy metal-polluted soil electricity based on electronic geotextiles promotees drip washing removal device and method
CN106623408A (en) * 2016-12-27 2017-05-10 常州大学 Electrokinetic remediation technology and method for removing heavy metal contaminated soil
CN106881339A (en) * 2017-02-22 2017-06-23 长江水利委员会长江科学院 Pin-connected panel original position drip washing is electronic with EKG to cooperate with the device and method for removing heavy metal-polluted soil
CN108687130A (en) * 2018-06-22 2018-10-23 中节能大地环境修复有限公司 A kind of method of nitrobenzene in oxidation soil
CN108906851A (en) * 2018-07-09 2018-11-30 北京中岩大地科技股份有限公司 A kind of high-moisture low-permeability waste residue removes saline and alkaline dehydration combined governance method
CN108994046A (en) * 2018-07-09 2018-12-14 北京中岩大地科技股份有限公司 A kind of dehydrated in situ of low-permeability high-moisture waste residue removes saline and alkaline method
CN109622597A (en) * 2019-01-24 2019-04-16 天津友爱环保科技有限公司 A kind of electrochemical repair method of heavy-metal contaminated soil
CN109622598B (en) * 2019-01-29 2021-09-07 华中农业大学 Method for repairing heavy metal contaminated soil based on principle of primary battery
CN109622598A (en) * 2019-01-29 2019-04-16 华中农业大学 A method of based on galvanic principles restoration of soil polluted by heavy metal
CN109772881A (en) * 2019-03-06 2019-05-21 韶关学院 A method of Cd-polluted farmland soil is repaired and efficiently utilized using fragrant plant
CN109772881B (en) * 2019-03-06 2021-11-05 韶关学院 Method for restoring farmland soil polluted by cadmium by utilizing aromatic plants and efficiently utilizing cadmium
CN109848203A (en) * 2019-03-23 2019-06-07 中国农业科学院农田灌溉研究所 A kind of restorative procedure for Cadmium in Soil of degrading
CN110510709A (en) * 2019-08-06 2019-11-29 东华大学 A kind of removable Cd2+Primary battery and its application
CN112692051A (en) * 2021-01-25 2021-04-23 明志科技大学 Method and equipment for removing pollutants by using beneficial microorganism mixed bacterial liquid
CN113385527A (en) * 2021-05-31 2021-09-14 山东大学 Method and device for repairing heavy metal contaminated soil suspension by adopting pulse current
CN113385527B (en) * 2021-05-31 2022-04-01 山东大学 Method and device for repairing heavy metal contaminated soil by adopting pulse current
CN116425315A (en) * 2023-05-25 2023-07-14 中交第三公路工程局有限公司 Constructed wetland system based on electrodynamic strengthening denitrification

Similar Documents

Publication Publication Date Title
CN101138767A (en) Method for renovating soil polluted by heavy metal
CN102941217B (en) Electric power repairing device and method for cylindrical arrangement electrode
CN106140809B (en) A kind of device and method using combination electrode repairing polluted soil and underground water
CN102500610A (en) Electrodynamic and drop-irrigation combined heavy-metal-polluted soil remediation method
CN104909526B (en) Device for removing heavy metals in sludge by using electro-dynamic method and synchronously and deeply dehydrating sludge
CN105855285B (en) A kind of device and method that rotation migration joint PRB repairs trichloro ethylene contaminated soil
LU101743A1 (en) Device and Method for In-situ Electro-kinetic Remediation and Consolidation of Contaminated Ultra-soft Soil
CN104492796A (en) Electrokinetic remediation method of heavy metal contaminated soil
CN107298489A (en) The method that high calcium high chloride ion coexists in electrochemical reactor and removal waste water
CN107008744A (en) A kind of method and soil remediation method for removing heavy metal in soil
CN110369490B (en) Heavy metal contaminated soil remediation device and remediation method
CN206316141U (en) A kind of processing unit of electro reclamation heavy-metal contaminated soil
CN105537261A (en) Electric force-fuel cell coupling device and restoring method for contaminated soil
CN106424117A (en) Device for electro-kinetic remediation of heavy metal contaminated soil by utilizing copper salt reinforced cathode
CN205042873U (en) Heavy metal contaminated soil processing system
CN110877045A (en) Tubular activated carbon air cathode, soil microorganism electrochemical restoration device, restoration method and application
CN104959378A (en) Bipolar-membrane electrolytic tank capable of removing heavy metal cations in soil
CN210231002U (en) Solar-driven ex-situ automatic polluted soil remediation device
CN104030540A (en) Vacuum-filtration and electric-dehydration sludge treating method
CN205413907U (en) Purifier of oils and heavy metal combined pollution cohesive soil earth
CN108545824B (en) Utilize the device and method of organic matter degradation self energizing processing Produced Water In Oil-gas Fields, Ngi
CN201799448U (en) Combined electrode
CN204934196U (en) One can remove the cationic bipolar membrane electrolytic cell of heavy metal in soil
CN105363774B (en) Soil Electroremediation devices and methods therefor based on rotation electrode
CN212469226U (en) Continuous automatic control's electronic prosthetic devices of heavy metal contaminated soil

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C02 Deemed withdrawal of patent application after publication (patent law 2001)
WD01 Invention patent application deemed withdrawn after publication

Open date: 20080312