CN105598144A - Restoration method of polluted soil - Google Patents

Restoration method of polluted soil Download PDF

Info

Publication number
CN105598144A
CN105598144A CN201610171376.8A CN201610171376A CN105598144A CN 105598144 A CN105598144 A CN 105598144A CN 201610171376 A CN201610171376 A CN 201610171376A CN 105598144 A CN105598144 A CN 105598144A
Authority
CN
China
Prior art keywords
soil
restorative procedure
contaminated
contaminated soil
acid
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
CN201610171376.8A
Other languages
Chinese (zh)
Other versions
CN105598144B (en
Inventor
徐大勇
洪亚军
操沛沛
裘秀群
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.)
Liuzhou Longjiang Hydropower Construction Co Ltd
Original Assignee
Anhui Polytechnic University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Anhui Polytechnic University filed Critical Anhui Polytechnic University
Priority to CN201610171376.8A priority Critical patent/CN105598144B/en
Publication of CN105598144A publication Critical patent/CN105598144A/en
Application granted granted Critical
Publication of CN105598144B publication Critical patent/CN105598144B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

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
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C1/00Reclamation of contaminated soil
    • B09C1/10Reclamation of contaminated soil microbiologically, biologically or by using enzymes
    • B09C1/105Reclamation of contaminated soil microbiologically, biologically or by using enzymes using fungi or plants
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C2101/00In situ

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Mycology (AREA)
  • Soil Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Health & Medical Sciences (AREA)
  • Botany (AREA)
  • Biomedical Technology (AREA)
  • Biotechnology (AREA)
  • General Health & Medical Sciences (AREA)
  • Microbiology (AREA)
  • Molecular Biology (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The invention relates to a restoration method of polluted soil. The restoration method comprises the following steps: adding an extracting solution into the polluted soil to extract heavy metals in the polluted soil, planting wetland plants in the polluted soil, and obtaining the plants with enrichment of the heavy metals after one growing season. The restoration method has the advantages that the heavy metals in the soil are extracted in situ, and aquatic plants are used for absorbing the heavy metals enriched in the extracting solution, so that the aftertreatment problem of the leached liquid from soil extraction and the problem of loss of nutrient components such as nitrogen, phosphorus and potassium and the like in the soil after soil extraction are solved; and an innovative idea and an innovative path are provided for restoring the soil polluted by the heavy metals.

Description

A kind of restorative procedure of contaminated soil
Technical field
The invention belongs to environmental improvement technical field, be specifically related to a kind of restorative procedure of contaminated soil, be specially adapted to heavilyThe soil of serious pollution in metal small size.
Background technology
The situation is tense for China's heavy metal pollution of soil, presents arable land heavy metal pollution serious, industrial and mining area and ambient contamination thereofThe features such as aggravation and high background value regional soil heavy metals exceeding standard. Number of ways causes sending out of heavy metal pollution of soil phenomenonRaw, the exploitation of for example heavy metal, smelting, sewage irrigation, containing using of heavy metal fertilizer, agricultural chemicals, and special groundGeochemistry circulation etc. Heavy metal has the notable features such as toxicity is large, incubation period long and can be bioaccumulation, once soilContaminated by heavy metals, certainly will amplify and have a strong impact on human health by the accumulation of food chain. Meanwhile, heavy metal-polluted soil dirtDye the pollution that also can directly cause by the Transport And Transformation of himself water environment and air ambient.
The restorative procedure of heavy metal-polluted soil is numerous, but only has two kinds from fundamental way classification, once being by heavy metal-polluted soilGround immobilization or Passivation Treatment, make it change invalid state into from available state, enters food chain and periphery thereby reduce heavy metalThe risk of environment. The 2nd, utilize the method such as chemical extraction or bio-absorbable, heavy metal is removed from soil, thoroughly reduceThe total amount of heavy metal-polluted soil. Last approach does not reduce heavy metal-polluted soil total amount, in the situation that condition is suitable, and soil weightMetal has the possibility being reactivated. Then an approach, because heavy metal has been shifted out to soil, fundamentally solves a soil huge sum of moneyBelong to pollution problem.
Chemical leaching method is exactly a kind of method of effective minimizing heavy metal-polluted soil total amount. It utilizes different digestion agents to make a huge sum of moneyBelong to and move to liquid phase from solid phase of soil, and reach by the discharge of leachate the object that reduces heavy metal-polluted soil. Soil soaksThe technology of carrying is applicable to the small size soil remediation of serious pollution in heavy metal, can reach efficient, quick to heavy metal-polluted soilThe object of removing. However, still Shortcomings part of soil lixiviate removal heavy metal at present, for example, soil lixiviateImplementation process soil need to be moved away from original position, and soil extract contains the further processing of a large amount of heavy metal needs and soil soaksPutting forward the nutritional labelings such as rear Soil Nitrogen, phosphorus and potassium can run off etc. to some extent. Above-mentioned not enough can increase soil remediation cost and cause afterThe problem of the continuous agricultural nutrient deficiency of soil.
Summary of the invention
For the deficiencies in the prior art, the invention provides a kind of restorative procedure of contaminated soil, by the weight in original position lixiviate soilMetal, absorb the heavy metal in enrichment leaching liquor with water plant, solved post processing problem that soil lixiviate drenches fluid andThe problem that after soil lixiviate, the nutritional labeling such as Soil Nitrogen, phosphorus and potassium can run off. For the reparation of heavy-metal contaminated soil providesArticle one, open one's minds and approach.
The technical solution adopted for the present invention to solve the technical problems is:
A restorative procedure for contaminated soil, step comprises:
A, contaminated soil is dug out and is backfilling in antiseepage heatable adobe sleeping platform after treatment;
B, digestion agent and water are made into extracting solution join in contaminated soil, make soil pH between 5-6.5, and makeSolution exceeds soil surface 5-25cm, lixiviate Heavy Metals in Contaminated Soils;
C, wetland plant is planted in contaminated soil, and make contaminated soil in water logging state, after 1 growth season, gather in the cropsThe plant of enriching heavy metal.
In described steps A, antiseepage treatment step is: barrier film on contaminated soil surrounding ground pad, and by the dirt of digging outDying soil is stacked on barrier film; Spread can natural degradation plastics thin digging out the heatable adobe sleeping platform surrounding that forms after soil and bottomFilm, after by the soil digging out again landfill in heatable adobe sleeping platform, and around heatable adobe sleeping platform, build the high enclosure wall of 0.5-1.0m, can natural degradationPlastic sheeting extends to body of wall top;
In described step B, digestion agent is organic acid and/or hydrochloric acid; Described digestion agent is pure for analyzing, the extracting solution preparingPH is 4-6; Described organic acid is selected from one or more in citric acid, malic acid, acetic acid, tartaric acid; Described soakingThe extraction time of carrying Heavy Metals in Contaminated Soils is 48-72h, maintains soil liquid pH5-6.5 constant during lixiviate;
In affiliated step C, wetland plant is iris or water hyacinth; Iris is yellow flag.
The invention has the beneficial effects as follows:
The present invention is directed to current chemical leaching method and process the deficiency of heavy-metal contaminated soil, developed a kind of soil lixiviate associating wetlandThe method of plant original position repairing heavy metal in soil, is easy to engineering construction, environmental friendliness, has following advantage simultaneously:
1) adopt the processing of biodegradable films bed course, ensure soil in-situ lixiviate, saved soil landed cost.
2) at soil leaching process, utilize wetland plant synchronously to process soil extract, solve containing after heavy metal soil extractThe problem of processing has improved efficiency simultaneously.
3) adopt not saliferous organic acid or hydrochloric acid as digestion agent, avoided the inhibition of leachate self to plant growth.
4) this method plant soil restoration cycle shorter, have that cost is low, non-secondary pollution, and plant can conserve water and soil,Increase soil fertility, and then accelerate the advantage of ecosystem self-regeneration, reach a soil huge sum of money by the results of plant simultaneouslyBelong to the object of thoroughly repairing.
Detailed description of the invention
Carry out further instruction below in conjunction with specific embodiment.
Embodiment 1
The present invention is directed to the soil that area is less, heavy metal pollution is comparatively serious and carry out, first take measures to utilize digestion agent formerPosition lixiviate, after the wetland plant repairing heavy metal in soil of planting. This working of an invention step is: the first step: first at Polluted SoilBarrier film on earth surrounding ground pad, then digs contaminated soil according to the purposes of soil after the heavy metal pollution degree of depth and reparationGo out, dig out soil and be stacked on barrier film, prevent the pollution to Soil Surrounding. Second step: form digging out after soilHeatable adobe sleeping platform surrounding and bottom spread thermoplastic starch plastic film, after by the soil digging out again landfill in heatable adobe sleeping platform, andThe high enclosure wall of heatable adobe sleeping platform top surrounding brick work 0.5m, biodegradable plastic film extends to body of wall top to do antiseepage. The 3rdStep: selecting citric acid digestion agent and water to be made into pH is 4.5 solution, solution is poured over to the heatable adobe sleeping platform of landfill contaminated soilIn, make lixiviate soil pH between 5-5.5, and make solution exceed soil surface 10cm. The 4th step: keep soil to soakCarry process 48h, maintain during this time soil liquid pH5-5.5 constant. The 5th step: select the wet of acidproof and energy enriching heavy metalGround plant yellow flag is planted in lixiviate soil, protects during this time by adding heavy metal free polluted river water, pond water or running waterHold waterlogging state. The 6th step: gather in the crops plant after 1 growth season, remove heatable adobe sleeping platform surrounding leakage proof wall.
Contaminated soil after Check processing, heavy metal in soil ion Cr, Pb, Cu, Cd concentration by 5.67mg/Kg,21.72mg/Kg, 11.43mg/Kg, 7.56mg/Kg reduce to respectively 0.51mg/Kg, 0.33mg/Kg, 1.12mg/Kg,0.23mg/Kg。
Embodiment 2
The present invention is directed to the soil that area is less, heavy metal pollution is comparatively serious and carry out, first take measures to utilize digestion agentOriginal position lixiviate, after the wetland plant repairing heavy metal in soil of planting. This working of an invention step is: the first step: first pollutingBarrier film on soil surrounding ground pad, then according to the heavy metal pollution degree of depth and after repairing the purposes of soil by contaminated soilDig out, dig out soil and be stacked on barrier film, prevent the pollution to Soil Surrounding. Second step: digging out shape after soilBecome heatable adobe sleeping platform surrounding and bottom spread thermoplastic starch plastic film, after by the soil digging out again landfill in heatable adobe sleeping platform, andAt the high enclosure wall of heatable adobe sleeping platform top surrounding brick work 0.5m, biodegradable plastic film extends to body of wall top to do antiseepage. TheThree steps: select malic acid, acetic acid, tartaric acid, hydrochloric acid digestion agent and water wiring solution-forming, malic acid, acetic acid, tartaric acid,Hydrochloric acid solution pH value is 5-6; Solution is poured in the heatable adobe sleeping platform of landfill contaminated soil, makes lixiviate soil pH at 6-6.5Between, and make solution exceed soil surface 10cm. The 4th step: keep soil leaching process 60h, maintain during this time soilPH value of solution 6-6.5 is constant. The 5th step: select wetland plant water hyacinth acidproof and energy enriching heavy metal to plant in lixiviate soilIn earth, keep waterlogging state by adding heavy metal free polluted river water, pond water or running water during this time. The 6th step:After 1 growth season, gather in the crops plant, remove heatable adobe sleeping platform surrounding leakage proof wall.
Contaminated soil after Check processing, heavy metal in soil ion Cr, Pb, Cu, Cd concentration by 5.67mg/Kg,21.72mg/Kg, 11.43mg/Kg, 7.56mg/Kg reduce to respectively 0.57mg/Kg, 0.46mg/Kg, 1.32mg/Kg,0.34mg/Kg。

Claims (7)

1. a restorative procedure for contaminated soil, step comprises:
A, contaminated soil is dug out and is backfilling in antiseepage heatable adobe sleeping platform after treatment;
B, digestion agent and water are made into extracting solution join in contaminated soil, make soil pH between 5-6.5, and makeSolution exceeds soil surface 5-25cm, lixiviate Heavy Metals in Contaminated Soils;
C, wetland plant is planted in contaminated soil, and make contaminated soil in water logging state, after 1 growth season, gather in the cropsThe plant of enriching heavy metal.
2. restorative procedure as claimed in claim 1, is characterized in that: in described steps A, antiseepage treatment step is:Barrier film on contaminated soil surrounding ground pad, is stacked in the contaminated soil digging out on barrier film; Digging out after soilSpread the heatable adobe sleeping platform surrounding forming and bottom can natural degradation plastic sheeting, after by the soil digging out again landfill in heatable adobe sleeping platform,And around heatable adobe sleeping platform, build the high enclosure wall of 0.5-1.0m, can extend to body of wall top by natural degradation plastic sheeting.
3. restorative procedure as claimed in claim 1, is characterized in that: in described step B digestion agent be organic acid and/orHydrochloric acid; Extracting solution pH is 4-6.
4. restorative procedure as claimed in claim 3, is characterized in that: described organic acid is selected from citric acid, malic acid, vinegarOne or more in acid, tartaric acid.
5. restorative procedure as claimed in claim 1, is characterized in that: when the lixiviate of described lixiviate Heavy Metals in Contaminated SoilsBetween be 48-72h, during lixiviate, maintain soil liquid pH5-6.5 constant.
6. restorative procedure as claimed in claim 1, is characterized in that: in affiliated step C, wetland plant is that Jris is plantedThing or water hyacinth.
7. restorative procedure as claimed in claim 6, is characterized in that: described iris is yellow flag.
CN201610171376.8A 2016-03-22 2016-03-22 A kind of restorative procedure of contaminated soil Active CN105598144B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610171376.8A CN105598144B (en) 2016-03-22 2016-03-22 A kind of restorative procedure of contaminated soil

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610171376.8A CN105598144B (en) 2016-03-22 2016-03-22 A kind of restorative procedure of contaminated soil

Publications (2)

Publication Number Publication Date
CN105598144A true CN105598144A (en) 2016-05-25
CN105598144B CN105598144B (en) 2019-01-18

Family

ID=55978792

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610171376.8A Active CN105598144B (en) 2016-03-22 2016-03-22 A kind of restorative procedure of contaminated soil

Country Status (1)

Country Link
CN (1) CN105598144B (en)

Cited By (23)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105935693A (en) * 2016-05-30 2016-09-14 青岛理工大学 Heavy-pollution site Sb in-situ and off-site coupling detoxication method
CN105945052A (en) * 2016-05-30 2016-09-21 青岛理工大学 Heavily-polluted site Pb in-situ and ex-situ couplingdetoxificationmethod
CN105945043A (en) * 2016-07-10 2016-09-21 中山市绿浪助剂有限公司 Method for rapidly treating heavy metal pollution of soil
CN105945047A (en) * 2016-07-10 2016-09-21 中山市绿浪助剂有限公司 Comprehensive remediation method for soil polluted by heavy metals and application of comprehensive remediation method
CN105945055A (en) * 2016-05-30 2016-09-21 青岛理工大学 Heavily-polluted site Hg in-situ and ex-situ coupling detoxification method based on biogas residues
CN105945056A (en) * 2016-05-30 2016-09-21 青岛理工大学 Heavy-polluted site Cd in-situ and ectopic coupling detoxification method based on biogas residues
CN105945065A (en) * 2016-05-30 2016-09-21 青岛理工大学 Heavily-polluted site Cu in-situ and ex-situ coupling detoxification method based on biogas residues
CN105964684A (en) * 2016-05-30 2016-09-28 青岛理工大学 Heavy pollution site Cd in-situ and off-site coupling detoxification method
CN106001088A (en) * 2016-05-30 2016-10-12 青岛理工大学 Pb in-situ and heterotopic coupling detoxifying method for heavily-contaminated site based on biogas residues
CN106001087A (en) * 2016-05-30 2016-10-12 青岛理工大学 Hg in-situ and heterotopic coupling detoxifying method for heavily-contaminated site
CN106001085A (en) * 2016-05-30 2016-10-12 青岛理工大学 Zn in-situ and heterotopic coupling detoxifying method for heavily-contaminated site
CN106040735A (en) * 2016-05-30 2016-10-26 青岛理工大学 Heavily-polluted site Cu in-situ and ex-situ coupling detoxifying method
CN106040736A (en) * 2016-05-30 2016-10-26 青岛理工大学 Biogas-residue-based in-situ and heterotopic coupling detoxication method for Sb of heavily-polluted site
CN106269831A (en) * 2016-08-30 2017-01-04 夏百庆 A kind of method of quick improvement heavy metal pollution of soil
CN106269822A (en) * 2016-08-22 2017-01-04 李荣华 One utilizes super enriching plant Huang gland perfume (or spice) green grass or young crops remediating heavy metal lead-contaminated soil method
CN107159692A (en) * 2017-06-30 2017-09-15 中冶华天工程技术有限公司 Heavy metal pollution place disposal system and method
CN107446584A (en) * 2016-05-30 2017-12-08 青岛理工大学 A kind of Cr VI place based on biogas residue is in situ and dystopy couples detoxification
CN107695087A (en) * 2017-10-19 2018-02-16 福州清河源环保科技有限公司 A kind of method of restoration of the ecosystem heavy-metal contaminated soil
CN108130096A (en) * 2017-12-28 2018-06-08 铁汉山艺环境建设有限公司 A kind of matrix for improving water plant wetland soil acidity
CN109454091A (en) * 2018-11-16 2019-03-12 长沙凯天工研院环保服务有限公司 A kind of aerobic compost and microwave leaching technology combination handle aging refuse landfill method humous
CN109909292A (en) * 2019-02-27 2019-06-21 安徽农业大学 A method of utilizing enrichment flowers iris rehabilitating soil lead contamination
CN110756576A (en) * 2019-09-12 2020-02-07 金晨辉 Soil replacement lead removal method for soil lead pollution treatment
CN113510144A (en) * 2021-04-22 2021-10-19 贵州星硕铭越环保科技有限公司 Method for treating heavy metal pollution of agricultural land in zinc smelting pollution area by soil method

Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0619764A1 (en) * 1991-10-03 1994-10-19 Cognis Inc Process for removing heavy metals from soils.
JP2002307048A (en) * 2001-04-16 2002-10-22 Mitsubishi Materials Corp Soil cleaning method and soil cleaning apparatus
CN101279325A (en) * 2008-04-22 2008-10-08 华南农业大学 Method for repairing heavy metal polluted soil using combined technology of interacted plants and chemical leaching
CN102974602A (en) * 2012-11-27 2013-03-20 河海大学 Heavy metal polluted soil remediation device and method
CN102989754A (en) * 2012-12-20 2013-03-27 江苏省中国科学院植物研究所 Method for enhanced remediation of copper contaminated soil by using iris in combination with cutting measure
CN103111463A (en) * 2013-02-01 2013-05-22 深圳市先科环保有限公司 Remediation method of heavy metal contaminated soil
CN103203353A (en) * 2013-01-22 2013-07-17 华南农业大学 Method for restoring moderately Cd-contaminated soil by using vine and melon vegetables and light eluting agent
CN103357655A (en) * 2013-07-15 2013-10-23 南京农业大学 Composite chemical leaching method for remediation of heavy metal contaminated soil
CN104324934A (en) * 2014-11-20 2015-02-04 东莞市环境科学研究所 Ecological remediation device and method for electroplating waste land polluted soil
CN104550207A (en) * 2013-10-12 2015-04-29 南京科盛环保科技有限公司 Novel method for metal-polluted soil restoration by plant
CN104607453A (en) * 2015-02-02 2015-05-13 陕西科技大学 Reinforced plant restoration method for lead-cadmium composite contaminated soil

Patent Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0619764A1 (en) * 1991-10-03 1994-10-19 Cognis Inc Process for removing heavy metals from soils.
JP2002307048A (en) * 2001-04-16 2002-10-22 Mitsubishi Materials Corp Soil cleaning method and soil cleaning apparatus
CN101279325A (en) * 2008-04-22 2008-10-08 华南农业大学 Method for repairing heavy metal polluted soil using combined technology of interacted plants and chemical leaching
CN102974602A (en) * 2012-11-27 2013-03-20 河海大学 Heavy metal polluted soil remediation device and method
CN102989754A (en) * 2012-12-20 2013-03-27 江苏省中国科学院植物研究所 Method for enhanced remediation of copper contaminated soil by using iris in combination with cutting measure
CN103203353A (en) * 2013-01-22 2013-07-17 华南农业大学 Method for restoring moderately Cd-contaminated soil by using vine and melon vegetables and light eluting agent
CN103111463A (en) * 2013-02-01 2013-05-22 深圳市先科环保有限公司 Remediation method of heavy metal contaminated soil
CN103357655A (en) * 2013-07-15 2013-10-23 南京农业大学 Composite chemical leaching method for remediation of heavy metal contaminated soil
CN104550207A (en) * 2013-10-12 2015-04-29 南京科盛环保科技有限公司 Novel method for metal-polluted soil restoration by plant
CN104324934A (en) * 2014-11-20 2015-02-04 东莞市环境科学研究所 Ecological remediation device and method for electroplating waste land polluted soil
CN104607453A (en) * 2015-02-02 2015-05-13 陕西科技大学 Reinforced plant restoration method for lead-cadmium composite contaminated soil

Cited By (28)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106001088A (en) * 2016-05-30 2016-10-12 青岛理工大学 Pb in-situ and heterotopic coupling detoxifying method for heavily-contaminated site based on biogas residues
CN105935693B (en) * 2016-05-30 2021-02-23 上海洁壤环保科技有限公司 Sb in-situ and ectopic coupling detoxification method for heavily polluted site
CN106001087A (en) * 2016-05-30 2016-10-12 青岛理工大学 Hg in-situ and heterotopic coupling detoxifying method for heavily-contaminated site
CN106001085A (en) * 2016-05-30 2016-10-12 青岛理工大学 Zn in-situ and heterotopic coupling detoxifying method for heavily-contaminated site
CN105945055A (en) * 2016-05-30 2016-09-21 青岛理工大学 Heavily-polluted site Hg in-situ and ex-situ coupling detoxification method based on biogas residues
CN105945056A (en) * 2016-05-30 2016-09-21 青岛理工大学 Heavy-polluted site Cd in-situ and ectopic coupling detoxification method based on biogas residues
CN105945065A (en) * 2016-05-30 2016-09-21 青岛理工大学 Heavily-polluted site Cu in-situ and ex-situ coupling detoxification method based on biogas residues
CN105964684A (en) * 2016-05-30 2016-09-28 青岛理工大学 Heavy pollution site Cd in-situ and off-site coupling detoxification method
CN105945052B (en) * 2016-05-30 2020-10-27 青岛理工大学 Pb in-situ and ectopic coupling detoxification method for heavily polluted site
CN106001087B (en) * 2016-05-30 2020-10-23 青岛理工大学 Hg in-situ and ectopic coupling detoxification method for heavily polluted site
CN107446584A (en) * 2016-05-30 2017-12-08 青岛理工大学 A kind of Cr VI place based on biogas residue is in situ and dystopy couples detoxification
CN106040735A (en) * 2016-05-30 2016-10-26 青岛理工大学 Heavily-polluted site Cu in-situ and ex-situ coupling detoxifying method
CN106040736A (en) * 2016-05-30 2016-10-26 青岛理工大学 Biogas-residue-based in-situ and heterotopic coupling detoxication method for Sb of heavily-polluted site
CN105945052A (en) * 2016-05-30 2016-09-21 青岛理工大学 Heavily-polluted site Pb in-situ and ex-situ couplingdetoxificationmethod
CN105935693A (en) * 2016-05-30 2016-09-14 青岛理工大学 Heavy-pollution site Sb in-situ and off-site coupling detoxication method
CN106001085B (en) * 2016-05-30 2020-12-15 青岛理工大学 Zn in-situ and ectopic coupling detoxification method for heavily polluted site
CN105945047A (en) * 2016-07-10 2016-09-21 中山市绿浪助剂有限公司 Comprehensive remediation method for soil polluted by heavy metals and application of comprehensive remediation method
CN105945043A (en) * 2016-07-10 2016-09-21 中山市绿浪助剂有限公司 Method for rapidly treating heavy metal pollution of soil
CN106269822A (en) * 2016-08-22 2017-01-04 李荣华 One utilizes super enriching plant Huang gland perfume (or spice) green grass or young crops remediating heavy metal lead-contaminated soil method
CN106269831A (en) * 2016-08-30 2017-01-04 夏百庆 A kind of method of quick improvement heavy metal pollution of soil
CN107159692A (en) * 2017-06-30 2017-09-15 中冶华天工程技术有限公司 Heavy metal pollution place disposal system and method
CN107695087A (en) * 2017-10-19 2018-02-16 福州清河源环保科技有限公司 A kind of method of restoration of the ecosystem heavy-metal contaminated soil
CN108130096A (en) * 2017-12-28 2018-06-08 铁汉山艺环境建设有限公司 A kind of matrix for improving water plant wetland soil acidity
CN109454091A (en) * 2018-11-16 2019-03-12 长沙凯天工研院环保服务有限公司 A kind of aerobic compost and microwave leaching technology combination handle aging refuse landfill method humous
CN109909292A (en) * 2019-02-27 2019-06-21 安徽农业大学 A method of utilizing enrichment flowers iris rehabilitating soil lead contamination
CN109909292B (en) * 2019-02-27 2021-07-23 安徽农业大学 Method for repairing soil lead pollution by using enriched flower iris
CN110756576A (en) * 2019-09-12 2020-02-07 金晨辉 Soil replacement lead removal method for soil lead pollution treatment
CN113510144A (en) * 2021-04-22 2021-10-19 贵州星硕铭越环保科技有限公司 Method for treating heavy metal pollution of agricultural land in zinc smelting pollution area by soil method

Also Published As

Publication number Publication date
CN105598144B (en) 2019-01-18

Similar Documents

Publication Publication Date Title
CN105598144A (en) Restoration method of polluted soil
CN104259192B (en) A kind of Ecological waterscape repair system of heavy metal pollution agricultural land soil and method
CN104550208B (en) A kind of farmland soil heavy metals pollution amelioration method of coupling activation and passivation
CN101462117B (en) Combined reinforced method for repairing cadmium polluted soil
CN105013812B (en) A kind of quick technology for repairing heavy metals in farmland pollution
CN101249501B (en) Plants repairing method based on uranium tail SLAG pollution
CN107138511A (en) A kind of method of renovation of heavy metal polluted soil with combined
CN105945047A (en) Comprehensive remediation method for soil polluted by heavy metals and application of comprehensive remediation method
CN103406349B (en) Hybrid giant napier is utilized to repair the method for acid and heavy metal lead combined contamination soil
CN107971334A (en) A kind of method of more pools-algae water cyclic irrigation system repairing polluted soil
CN106171116A (en) A kind of coal-mining subsidence pools zone ecological agriculture reconstructing method
CN104668281B (en) Chemical washing-plant absorbing combined repair method for cadmium heavy pollution acid soil of non-ferrous metal mining area of south China
CN103406350A (en) Method for remediating acid/heavy metal cadmium composite polluted soil by using Pennisetum hydridum
CN101224465B (en) Method of leaching and repairing cadmium polluted coast saline soil
CN106734150A (en) A kind of cycling elution system administered for farmland pollution soil remediation
CN102580987A (en) Method for improving phytoremediation efficiency of farmland soil with light cadmium pollution by using potash fertilizer
CN102372406A (en) Heavy-metal-polluted substrate sludge ex-situ repairing method
CN106180164B (en) Chelating agent slow-release body for heavy metal soil remediation
CN101332466A (en) Method for repairing heavy metal pollution in mine soil and sludge
CN105665439A (en) Practical method for farmland soil cadmium pollution remediationby planting Salix jiangsuensis J795
CN101961725A (en) Application of dockleaf knotweed to remediation of heavy metal pollution of mine soil and sludge
CN104550219B (en) Method for repairing contaminated soil through arranging powder ridge underdrain system
Percy et al. Landfill leachate disposal with irrigated vetiver grass
CN101961726B (en) Application of malva for remediation of cadmium and lead pollution of mine soil and sludge
CN209255465U (en) A kind of ecological elution circuit administered for heavy-metal contaminated soil or slag

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
TR01 Transfer of patent right

Effective date of registration: 20190515

Address after: 530000 45 Nanning, Xiangyi Road, XiXiangTang District, the Guangxi Zhuang Autonomous Region

Patentee after: GUANGXI CONSTRUCTION ENGINEERING GROUP UNITED CONSTRUCTION CO., LTD.

Address before: 241000 Beijing Middle Road, Jiujiang District, Wuhu City, Anhui Province

Patentee before: Anhui Polytechnic University

TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20200416

Address after: No. 19-17, bahuijin international, No. 106, Yuejin Road, Liuzhou City, Guangxi Zhuang Autonomous Region

Patentee after: Liuzhou Longjiang Hydropower Construction Co., Ltd

Address before: 530000 the Guangxi Zhuang Autonomous Region XiXiangTang Nanning fraternity Road No. 45

Patentee before: GUANGXI CONSTRUCTION ENGINEERING GROUP UNITED CONSTRUCTION Co.,Ltd.

TR01 Transfer of patent right