CN105945044A - Non-destructive repairing method for heavy metal contaminated soil - Google Patents

Non-destructive repairing method for heavy metal contaminated soil Download PDF

Info

Publication number
CN105945044A
CN105945044A CN201610315697.0A CN201610315697A CN105945044A CN 105945044 A CN105945044 A CN 105945044A CN 201610315697 A CN201610315697 A CN 201610315697A CN 105945044 A CN105945044 A CN 105945044A
Authority
CN
China
Prior art keywords
soil
heavy
heavy metal
carboxylic acid
lossless
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.)
Withdrawn
Application number
CN201610315697.0A
Other languages
Chinese (zh)
Inventor
王文庆
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.)
Dongguan Lianzhou Intellectual Property Operation and Management Co Ltd
Original Assignee
Dongguan Lianzhou Intellectual Property Operation and Management Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Dongguan Lianzhou Intellectual Property Operation and Management Co Ltd filed Critical Dongguan Lianzhou Intellectual Property Operation and Management Co Ltd
Priority to CN201610315697.0A priority Critical patent/CN105945044A/en
Publication of CN105945044A publication Critical patent/CN105945044A/en
Withdrawn legal-status Critical Current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
    • B09C1/02Extraction using liquids, e.g. washing, leaching, flotation

Abstract

The invention discloses a non-destructive repairing method for heavy metal contaminated soil. The method comprises the steps that to-be-treated soil is broken through a rotary cultivator; then, irrigation is conducted, and part of heavy metal fixed in soil is dissolved out; nanometer particles with Fe3O4 as a core and SiO2 as a shell are added into the soil to serve as adsorbent, and nitrogen containing macro-ring carboxylic acid derivate is modified on the edge of the shell of the particles of a core and shell structure; after adsorption treatment, the adsorbent adsorbing the heavy metal is separated out through an electromagnetic harrow device, a buffer solution and carbon microspheres are added in the separated-out soil, stirring and standing are conducted, and supernate is removed; and then, the soil is washed by purified water several times, and the treated soil is obtained. The soil treated through the method is free of secondary contamination, the heavy metal removing rate is high, efficiency is high, and cost is low.

Description

A kind of lossless restorative procedure of heavy-metal contaminated soil
Technical field:
The present invention relates to contaminated soil process field, be specifically related to the lossless reparation side of a kind of heavy-metal contaminated soil Method.
Background technology:
Along with China's industrialization, urbanization, the continuous quickening of the intensive process in rural area, heavy metal pollution of soil is asked Topic becomes increasingly conspicuous.In urban environment, owing to industry and mankind's activity bring substantial amounts of heavy metal into urban soil In, cause the accumulation in soil of these elements, and by air, water body or food chain directly or indirectly Threaten the health of the mankind.Therefore, soil pollution reparation has become the vital task of field of Environment Protection.
It is dirty that Chinese patent (201110360190.4) discloses a kind of nano zero valence iron-electromagnetism rake remediating heavy metal Dye soil/sludge processes, is to use Zero-valent Iron as adsorbent and to combine electromagnetism rake technology and effectively remove in soil Heavy metal, although the method can effectively remove the heavy metal in soil, but its adsorbance is little, rehabilitating soil Time adsorbent addition big, substantially increase the cost of soil remediation.
Summary of the invention:
It is an object of the invention to provide the lossless restorative procedure of a kind of heavy-metal contaminated soil, the method can be effective Heavy metal is separated, and efficiency is high, low cost.
For achieving the above object, the present invention is by the following technical solutions:
The lossless restorative procedure of a kind of heavy-metal contaminated soil, comprises the following steps:
(1) by one block of dry soil by heavy metal pollution, crush with rotary cultivator, top layer 0.5-1m Soil breaking reach 10-15cm to diameter less than the soil block of 3mm, the hydrops layer irrigated to soil horizon, Stir 10-20h at 25-30 DEG C, make the part leaching ability of heavy metal being fixed in soil;
(2) soil after step (1) is irrigated adds Fe3O4For nuclear core, SiO2Nano-particle for shell As adsorbent, the shell edge of this core-shell structure particles is modified with nitrogen heterocyclic ring carboxylic acid derivates, at 25-30 DEG C Lower stirring 5-10h, then uses electromagnetism rake device to be separated by the adsorbent being adsorbed with heavy metal, and to dividing Soil after from adds buffer, is simultaneously introduced carbosphere, mechanical agitation 20-40min, stands 10-15h, Remove supernatant, 2-3 time the most repeatedly, finally use pure water soil 1-3 time, the soil after being governed.
Preferred as technique scheme, in step (2), the ring bone of described nitrogen heterocyclic ring carboxylic acid derivates Containing atom N on frame, the atom N on ring skeleton is connected with carboxyl arm, and described carboxyl arm is positioned at outside ring.
Preferred as technique scheme, in step (2), described nitrogen heterocyclic ring carboxylic acid derivates is Isosorbide-5-Nitrae, 7- 7-triazacyclononane-1,4,7-triacetic acid, Cyclen-1,4,7,10-tetraacethyl, 1,4,8,11-tetraazacyclododecane tetradecane-1,4,8,11-tetraacethyl, 1,4,7,10,13-five-nitrogen heterocyclic pentadecane -1,4,7,10,13-pentaacetic acid, 1,4,7,10,13,16-hexanitrogen heterocycle octadecane-1,4,7,10,13,16-six second One in acid.
Preferred as technique scheme, in step (2), the preparation method of described adsorbent includes following Step:
A nitrogen heterocyclic ring carboxylic acid derivates is dissolved in the biological buffer that pH is 5.3-5.5 by (), nitrogen is protected Protect down, add catalyst EDC HCl and NHS, stir 1.5-3h under room temperature, obtain nitrogen heterocyclic ring carboxylic acid and spread out Biological activated intermediate;
B () adds amino functional in the activated intermediate of the prepared nitrogen heterocyclic ring carboxylic acid derivates of step (a) The magnetic microsphere changed, after ultrasonic disperse, reacts 8-10h at 25 ± 5 DEG C, and reaction separates with Magnet after terminating Product, and replace cleaning product for several times with 0.1mol/L HCl solution, second alcohol and water, it is vacuum dried 10-20h, Obtain adsorbent.
Preferred as technique scheme, in step (b), the magnetic microsphere of described amino functional be with Fe3O4Magnetic nanoparticle is nuclear core, SiO2For protection shell, shell contains terminal amino group structure.
Preferred as technique scheme, in step (a), described nitrogen heterocyclic ring carboxylic acid derivates, EDC HCl, The mol ratio of NHS is 1:(10-40): (5-15).
Preferred as technique scheme, in step (a), described biological buffer solutions is 1mol/L's Quinoline ethyl sulfonic acid aqueous solution.
Preferred as technique scheme, in step (2), described buffer be concentration be 50-100mol/L Bodied ferric sulfate and concentration be the oxalic acid solution of 0.3-0.5mol/L be the mixture of 1:1 according to volume ratio.
Preferred as technique scheme, in step (2), the buffer of described addition and the body of carbosphere Long-pending ratio is (10-15): 1.
The method have the advantages that
Magnetic adsorbent prepared by the present invention, by the amidation process of EDC HCl, NHS catalysis, by azepine Macro ring carboxylic acid derivates modifies the SiO of magnetic composite microsphere2Shell edge, its excellent adsorption, can effectively remove Heavy metal ion in electroplating effluent, technique power consumption is low, can realize large-scale production, and its suction capacity is big, suction Attached speed is fast, and the total removal rate of heavy metal ion reaches more than 98%;
The present invention uses Fe3O4Magnetic nanoparticle is nuclear core, SiO2For protection shell, shell contains end ammonia The nano-particle of based structures is as adsorbent, and combines running vehicle type electromagnetism rake technology, effectively removes contaminated soil In heavy metal, efficiency is high, and processing cost is low, to soil non-secondary pollution.
Detailed description of the invention:
In order to be better understood from the present invention, below by embodiment, the present invention is further described, and embodiment is only used In explaining the present invention, the present invention will not be constituted any restriction.
Embodiment 1
The lossless restorative procedure of a kind of heavy-metal contaminated soil, comprises the following steps:
(1) preparation of adsorbent:
A 1mol 1,4,7-7-triazacyclononane-1,4,7-triacetic acid is dissolved in the life that pH is 5.3-5.5 by () In thing buffer, under nitrogen protection, add 10mol catalyst EDC HCl and 5molNHS, stir under room temperature 1.5h, obtains the activated intermediate of nitrogen heterocyclic ring carboxylic acid derivates;
B () adds Fe in the activated intermediate of the prepared nitrogen heterocyclic ring carboxylic acid derivates of step (a)3O4Magnetic Property nano-particle is nuclear core, SiO2For protection shell, shell contains the nano-particle of terminal amino group structure, super After sound dispersion, at 25 ± 5 DEG C, react 8h, reaction terminate after with Magnet separation product, and use 0.1mol/L HCl Solution, second alcohol and water replace cleaning product for several times, are vacuum dried 10h, obtain adsorbent;
(2) by one block of dry soil by heavy metal pollution, crush with rotary cultivator, top layer 0.5m's Soil breaking is less than the soil block of 3mm to diameter, and the hydrops layer irrigated to soil horizon reaches 10m, at 25-30 DEG C Lower stirring 10h, makes the part leaching ability of heavy metal being fixed in soil;
(3) soil after step (2) is irrigated adds the adsorbent that step (1) prepares, at 25-30 DEG C Lower stirring 5h, then uses electromagnetism rake device to be separated by the adsorbent being adsorbed with heavy metal, and after separating Soil in add the bodied ferric sulfate of 50mol/L with concentration be the oxalic acid solution of 0.3mol/L, both add Entering amount is that every 40kg soil is separately added into 2kg, 4kg, is simultaneously introduced 0.5kg carbosphere, mechanical agitation 20min, Stand 10h, remove supernatant, 2-3 time the most repeatedly, finally use pure water soil 1-3 time, controlled Soil after reason.
Embodiment 2
(1) preparation of adsorbent:
A () is by molten for 1mol 1,4,7,10,13,16-hexanitrogen heterocycle octadecane-1,4,7,10,13,16-six acetic acid Solution, in the biological buffer that pH is 5.3-5.5, under nitrogen protection, adds 40mol catalyst EDC HCl And 15molNHS, stir 3h under room temperature, obtain the activated intermediate of nitrogen heterocyclic ring carboxylic acid derivates;
B () adds Fe in the activated intermediate of the prepared nitrogen heterocyclic ring carboxylic acid derivates of step (a)3O4Magnetic Property nano-particle is nuclear core, SiO2For protection shell, shell contains the nano-particle of terminal amino group structure, super After sound dispersion, at 25 ± 5 DEG C, react 10h, reaction terminate after with Magnet separation product, and use 0.1mol/L HCl Solution, second alcohol and water replace cleaning product for several times, are vacuum dried 20h, obtain adsorbent;
(2) by one block of dry soil by heavy metal pollution, crush with rotary cultivator, the soil of top layer 1m Earth is crushed to the diameter soil block less than 3mm, and the hydrops layer irrigated to soil horizon reaches 15cm, at 25-30 DEG C Stirring 20h, makes the part leaching ability of heavy metal being fixed in soil;
(3) soil after step (2) is irrigated adds the adsorbent that step (1) prepares, at 25-30 DEG C Lower stirring 10h, then uses electromagnetism rake device to be separated by the adsorbent being adsorbed with heavy metal, and to separation After soil in add the bodied ferric sulfate of 100mol/L with concentration be the oxalic acid solution of 0.5mol/L, both Addition is that every 50kg soil is separately added into 5kg, 5kg, is simultaneously introduced 1kg carbosphere, mechanical agitation 40min, Stand 15h, remove supernatant, 2-3 time the most repeatedly, finally use pure water soil 1-3 time, controlled Soil after reason.
Embodiment 3
(1) preparation of adsorbent:
A 1mol Cyclen-1,4,7,10-tetraacethyl is dissolved in pH by () In the biological buffer of 5.3-5.5, under nitrogen protection, add 20mol catalyst EDC HCl and 7molNHS, Stir 1.8h under room temperature, obtain the activated intermediate of nitrogen heterocyclic ring carboxylic acid derivates;
B () adds Fe in the activated intermediate of the prepared nitrogen heterocyclic ring carboxylic acid derivates of step (a)3O4Magnetic Property nano-particle is nuclear core, SiO2For protection shell, shell contains the nano-particle of terminal amino group structure, super After sound dispersion, at 25 ± 5 DEG C, react 8.5h, reaction terminate after with Magnet separation product, and use 0.1mol/L HCl solution, second alcohol and water replace cleaning product for several times, are vacuum dried 12h, obtain adsorbent;
(2) by one block of dry soil by heavy metal pollution, crush with rotary cultivator, top layer 0.6m's Soil breaking is less than the soil block of 3mm to diameter, and the hydrops layer irrigated to soil horizon reaches 11cm, at 25-30 DEG C Lower stirring 12h, makes the part leaching ability of heavy metal being fixed in soil;
(3) soil after step (2) is irrigated adds the adsorbent that step (1) prepares, at 25-30 DEG C Lower stirring 6h, then uses electromagnetism rake device to be separated by the adsorbent being adsorbed with heavy metal, and after separating Soil in add the bodied ferric sulfate of 60mol/L with concentration be the oxalic acid solution of 0.35mol/L, both add Entering amount is that every 40kg soil is separately added into 3kg, 4.2kg, is simultaneously introduced 0.6kg carbosphere, mechanical agitation 25min, Stand 11h, remove supernatant, 2-3 time the most repeatedly, finally use pure water soil 1-3 time, controlled Soil after reason.
Embodiment 4
(1) preparation of adsorbent:
A 1mol 1,4,8,11-tetraazacyclododecane tetradecane-1,4,8,11-tetraacethyl is dissolved in pH by () In the biological buffer of 5.3-5.5, under nitrogen protection, add 25mol catalyst EDC HCl and 9molNHS, Stir 2h under room temperature, obtain the activated intermediate of nitrogen heterocyclic ring carboxylic acid derivates;
B () adds Fe in the activated intermediate of the prepared nitrogen heterocyclic ring carboxylic acid derivates of step (a)3O4Magnetic Property nano-particle is nuclear core, SiO2For protection shell, shell contains the nano-particle of terminal amino group structure, super After sound dispersion, at 25 ± 5 DEG C, react 9h, reaction terminate after with Magnet separation product, and use 0.1mol/L HCl Solution, second alcohol and water replace cleaning product for several times, are vacuum dried 14h, obtain adsorbent;
(2) by one block of dry soil by heavy metal pollution, crush with rotary cultivator, top layer 0.7m's Soil breaking is less than the soil block of 3mm to diameter, and the hydrops layer irrigated to soil horizon reaches 12cm, at 25-30 DEG C Lower stirring 14h, makes the part leaching ability of heavy metal being fixed in soil;
(3) soil after step (2) is irrigated adds the adsorbent that step (1) prepares, at 25-30 DEG C Lower stirring 7h, then uses electromagnetism rake device to be separated by the adsorbent being adsorbed with heavy metal, and after separating Soil in add the bodied ferric sulfate of 70mol/L with concentration be the oxalic acid solution of 0.4mol/L, both add Entering amount is that every 40kg soil is separately added into 3.5kg, 4.4kg, is simultaneously introduced 0.7kg carbosphere, mechanical agitation 30min, stands 12h, removes supernatant, 2-3 time the most repeatedly, finally uses pure water soil 1-3 time, Soil after being governed.
Embodiment 5
(1) preparation of adsorbent:
A 1mol 1,4,7,10,13-five-nitrogen heterocyclic pentadecane-1,4,7,10,13-pentaacetic acid is dissolved in pH by () For in the biological buffer of 5.3-5.5, under nitrogen protection, add 30mol catalyst EDC HCl and 11molNHS, stirs 2.5h, obtains the activated intermediate of nitrogen heterocyclic ring carboxylic acid derivates under room temperature;
B () adds Fe in the activated intermediate of the prepared nitrogen heterocyclic ring carboxylic acid derivates of step (a)3O4Magnetic Property nano-particle is nuclear core, SiO2For protection shell, shell contains the nano-particle of terminal amino group structure, super After sound dispersion, at 25 ± 5 DEG C, react 9.5h, reaction terminate after with Magnet separation product, and use 0.1mol/L HCl solution, second alcohol and water replace cleaning product for several times, are vacuum dried 16h, obtain adsorbent;
(2) by one block of dry soil by heavy metal pollution, crush with rotary cultivator, top layer 0.8m's Soil breaking is less than the soil block of 3mm to diameter, and the hydrops layer irrigated to soil horizon reaches 13cm, at 25-30 DEG C Lower stirring 16h, makes the part leaching ability of heavy metal being fixed in soil;
(3) soil after step (2) is irrigated adds the adsorbent that step (1) prepares, at 25-30 DEG C Lower stirring 8h, then uses electromagnetism rake device to be separated by the adsorbent being adsorbed with heavy metal, and after separating Soil in add the bodied ferric sulfate of 80mol/L with concentration be the oxalic acid solution of 0.45mol/L, both add Entering amount is that every 40kg soil is separately added into 4kg, 4.6kg, is simultaneously introduced 0.8kg carbosphere, mechanical agitation 35min, Stand 13h, remove supernatant, 2-3 time the most repeatedly, finally use pure water soil 1-3 time, controlled Soil after reason.
Embodiment 6
(1) preparation of adsorbent:
A () is by molten for 1mol 1,4,7,10,13,16-hexanitrogen heterocycle octadecane-1,4,7,10,13,16-six acetic acid Solution, in the biological buffer that pH is 5.3-5.5, under nitrogen protection, adds 35mol catalyst EDC HCl And 13molNHS, stir 2.8h under room temperature, obtain the activated intermediate of nitrogen heterocyclic ring carboxylic acid derivates;
B () adds Fe in the activated intermediate of the prepared nitrogen heterocyclic ring carboxylic acid derivates of step (a)3O4Magnetic Property nano-particle is nuclear core, SiO2For protection shell, shell contains the nano-particle of terminal amino group structure, super After sound dispersion, at 25 ± 5 DEG C, react 9.5h, reaction terminate after with Magnet separation product, and use 0.1mol/L HCl solution, second alcohol and water replace cleaning product for several times, are vacuum dried 18h, obtain adsorbent;
(2) by one block of dry soil by heavy metal pollution, crush with rotary cultivator, top layer 0.9m's Soil breaking is less than the soil block of 3mm to diameter, and the hydrops layer irrigated to soil horizon reaches 14cm, at 25-30 DEG C Lower stirring 18h, makes the part leaching ability of heavy metal being fixed in soil;
(3) soil after step (2) is irrigated adds the adsorbent that step (1) prepares, at 25-30 DEG C Lower stirring 9h, then uses electromagnetism rake device to be separated by the adsorbent being adsorbed with heavy metal, and after separating Soil in add the bodied ferric sulfate of 90mol/L with concentration be the oxalic acid solution of 0.45mol/L, both add Entering amount is that every 40kg soil is separately added into 4.5kg, 4.8kg, is simultaneously introduced 0.9kg carbosphere, mechanical agitation 40min, stands 14h, removes supernatant, 2-3 time the most repeatedly, finally uses pure water soil 1-3 time, Soil after being governed.

Claims (9)

1. the lossless restorative procedure of a heavy-metal contaminated soil, it is characterised in that comprise the following steps:
(1) by one block of dry soil by heavy metal pollution, crush with rotary cultivator, top layer The soil breaking of 0.5-1m is less than the soil block of 3mm to diameter, and the hydrops layer irrigated to soil horizon reaches 10-15cm, stirs 10-20h at 25-30 DEG C, makes the part leaching ability of heavy metal being fixed in soil;
(2) soil after step (1) is irrigated adds Fe3O4For nuclear core, SiO2Receiving for shell Rice grain is as adsorbent, and the shell edge of this core-shell structure particles is modified with nitrogen heterocyclic ring carboxylic acid and derives Thing, stirs 5-10h at 25-30 DEG C, then uses electromagnetism rake device will be adsorbed with the absorption of heavy metal Agent is separated, and adds buffer in the soil after separating, and is simultaneously introduced carbosphere, and machinery stirs Mix 20-40min, stand 10-15h, remove supernatant, 2-3 time the most repeatedly, finally wash with pure water Wash soil 1-3 time, the soil after being governed.
The lossless restorative procedure of a kind of heavy-metal contaminated soil the most as claimed in claim 1, its feature It is, in step (2), containing atom N on the ring skeleton of described nitrogen heterocyclic ring carboxylic acid derivates, ring Atom N on skeleton is connected with carboxyl arm, and described carboxyl arm is positioned at outside ring.
The lossless restorative procedure of a kind of heavy-metal contaminated soil the most as claimed in claim 1, its feature Being, in step (2), described nitrogen heterocyclic ring carboxylic acid derivates is Isosorbide-5-Nitrae, 7-7-triazacyclononane-Isosorbide-5-Nitrae, 7- Triacetic acid, Cyclen-1,4,7,10-tetraacethyl, 1,4,8,11-tetra-azepine The ring tetradecane-1,4,8,11-tetraacethyl, 1,4,7,10,13-five-nitrogen heterocyclic pentadecane-1,4,7,10,13- In pentaacetic acid, 1,4,7,10,13,16-hexanitrogen heterocycle octadecane-1,4,7,10,13,16-six acetic acid one Kind.
The lossless restorative procedure of a kind of heavy-metal contaminated soil the most as claimed in claim 1, its feature Being, in step (2), the preparation method of described adsorbent comprises the following steps:
A nitrogen heterocyclic ring carboxylic acid derivates is dissolved in the biological buffer that pH is 5.3-5.5 by (), Under nitrogen protection, add catalyst EDC HCl and NHS, stir 1.5-3h under room temperature, obtain azepine The activated intermediate of macro ring carboxylic acid derivates;
B () adds ammonia in the activated intermediate of the prepared nitrogen heterocyclic ring carboxylic acid derivates of step (a) The magnetic microsphere of base functionalization, after ultrasonic disperse, reacts 8-10h, after reaction terminates at 25 ± 5 DEG C With Magnet separation product, and replace cleaning product for several times with 0.1mol/L HCl solution, second alcohol and water, Vacuum drying 10-20h, obtains adsorbent.
The lossless restorative procedure of a kind of heavy-metal contaminated soil the most as claimed in claim 4, its feature Being, in step (b), the magnetic microsphere of described amino functional is with Fe3O4Magnetic nanoparticle is Nuclear core, SiO2For protection shell, shell contains terminal amino group structure.
The lossless restorative procedure of a kind of heavy-metal contaminated soil the most as claimed in claim 4, its feature Being, in step (a), described nitrogen heterocyclic ring carboxylic acid derivates, the mol ratio of EDC HCl, NHS are 1:(10-40): (5-15).
The lossless restorative procedure of a kind of heavy-metal contaminated soil the most as claimed in claim 4, its feature Being, in step (a), described biological buffer solutions is the morpholino b acid aqueous solution of 1mol/L.
The lossless restorative procedure of a kind of heavy-metal contaminated soil the most as claimed in claim 1, its feature Be, in step (2), described buffer be concentration be that the bodied ferric sulfate of 50-100mol/L is with dense Degree is the mixture of 1:1 for the oxalic acid solution of 0.3-0.5mol/L according to volume ratio.
The lossless restorative procedure of a kind of heavy-metal contaminated soil the most as claimed in claim 1, its feature Being, in step (2), the buffer of described addition and the volume ratio of carbosphere are (10-15): 1.
CN201610315697.0A 2016-05-12 2016-05-12 Non-destructive repairing method for heavy metal contaminated soil Withdrawn CN105945044A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610315697.0A CN105945044A (en) 2016-05-12 2016-05-12 Non-destructive repairing method for heavy metal contaminated soil

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610315697.0A CN105945044A (en) 2016-05-12 2016-05-12 Non-destructive repairing method for heavy metal contaminated soil

Publications (1)

Publication Number Publication Date
CN105945044A true CN105945044A (en) 2016-09-21

Family

ID=56912497

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610315697.0A Withdrawn CN105945044A (en) 2016-05-12 2016-05-12 Non-destructive repairing method for heavy metal contaminated soil

Country Status (1)

Country Link
CN (1) CN105945044A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109622581A (en) * 2018-12-28 2019-04-16 江西夏氏春秋环境股份有限公司 A method of Heavy Metals in Soil Contaminated is removed using magnetic modification biological charcoal
CN109794216A (en) * 2019-02-27 2019-05-24 福建工程学院 A kind of preparation of nano adsorption material and its application in repairing heavy metal in soil pollution

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003147444A (en) * 2001-11-09 2003-05-21 Nippon Parkerizing Co Ltd Method for recovering valuable metal from metal cyanide-containing solution
CN102500613A (en) * 2011-11-15 2012-06-20 同济大学 Process for restoring heavy metal contaminated soil/sludge through combining nanometer zero-valent iron with electromagnetic rake
CN103894396A (en) * 2014-03-24 2014-07-02 华南理工大学 Method for treating heavy metal contaminated soil
CN103894397A (en) * 2014-03-24 2014-07-02 华南理工大学 Method for carrying out three-level remediation on heavy metal contaminated soil
CN103962371A (en) * 2014-05-12 2014-08-06 福建工程学院 Nondestructive restoration method for polluted soil
CN104403675A (en) * 2014-09-28 2015-03-11 上海化工研究院 Soil repairing agent used for fixing heavy metal element in polluted soil, preparation method and application thereof

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003147444A (en) * 2001-11-09 2003-05-21 Nippon Parkerizing Co Ltd Method for recovering valuable metal from metal cyanide-containing solution
CN102500613A (en) * 2011-11-15 2012-06-20 同济大学 Process for restoring heavy metal contaminated soil/sludge through combining nanometer zero-valent iron with electromagnetic rake
CN103894396A (en) * 2014-03-24 2014-07-02 华南理工大学 Method for treating heavy metal contaminated soil
CN103894397A (en) * 2014-03-24 2014-07-02 华南理工大学 Method for carrying out three-level remediation on heavy metal contaminated soil
CN103962371A (en) * 2014-05-12 2014-08-06 福建工程学院 Nondestructive restoration method for polluted soil
CN104403675A (en) * 2014-09-28 2015-03-11 上海化工研究院 Soil repairing agent used for fixing heavy metal element in polluted soil, preparation method and application thereof

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
CHIH-CHIA HUANG ET AL: "Enhancing transversal relaxation for magnetite nanoparticles in MR imaging using Gd3+-chelated mesoporous silica shells", 《ACS NANO》 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109622581A (en) * 2018-12-28 2019-04-16 江西夏氏春秋环境股份有限公司 A method of Heavy Metals in Soil Contaminated is removed using magnetic modification biological charcoal
CN109794216A (en) * 2019-02-27 2019-05-24 福建工程学院 A kind of preparation of nano adsorption material and its application in repairing heavy metal in soil pollution

Similar Documents

Publication Publication Date Title
CN106799211B (en) A kind of compound mercury-removing adsorbent of attapulgite-cross-linked chitosan and its solid phase synthesis process
CN105903438B (en) A kind of attapulgite and the compound adsorbent and preparation method thereof of graphene oxide
CN107442082B (en) A kind of magnetism polyacrylamide/alginic acid zirconium gel ball and its preparation method and application
CN107362777B (en) A kind of preparation method of magnetism stalk cellulose adsorbent for heavy metal
CN105289513B (en) One kind removes Hg2+Magnetic oxygenated graphene adsorbent of the citric acid modification of ion and preparation method thereof
CN106984290A (en) The preparation method of the chitosan of adsorbing heavy metal ions/sodium alginate magnetic composite microsphere
CN106745645A (en) The preparation method and applications of nano zero-valence iron composite material
CN104587956B (en) A kind of preparation method being coated with the graphene oxide composite granule coated nano zero valence iron as carrier with multilamellar activated carbon
CN107626283B (en) Utilize the method for antibiotic in multi-walled carbon nanotube/metal organic framework composite material adsorbed water body
CN106492761A (en) A kind of preparation method of magnetic hydrogel microsphere
CN105457601B (en) The preparation and application of a kind of magnetic oxygenated graphene adsorbent of modified with folic acid
CN109894095B (en) Sodium alginate-chitosan composite gel microsphere adsorption arsenic removal material containing iron and manganese oxides and preparation method thereof
CN104014314B (en) Bio-adsorbent, preparation method and application
CN108855083A (en) A method of sulfa drugs in water removal is removed with modified zeolite activation Peracetic acid
CN109534432A (en) The preparation method of the biological carbon modified material of phosphorus in a kind of removal eutrophication water
CN104888706A (en) Magnetically separable compound adsorbent as well as preparation method and application thereof
CN108671886A (en) A kind of magnetic active carbon adsorbent and the preparation method and application thereof based on abandoned biomass
CN109967029A (en) For removing graphene oxide/attapulgite magnetic composite material preparation method of inderal in water body
CN105945044A (en) Non-destructive repairing method for heavy metal contaminated soil
CN108772038B (en) Adsorbent for removing lead ions in water and preparation method and application thereof
CN105289514B (en) A kind of preparation and application of the magnetic oxygenated graphene adsorbent of 1-hydroxy ethylidene-1,1-diphosphonic acid modification
CN110339818A (en) A kind of preparation method of modified magnetic chitosan absorbent
CN109317110A (en) A kind of application for preparing and its going copper ion in water removal of sodium alginate/smectite composite gel material
CN106745592B (en) It is a kind of with heavy metal ion adsorbed and detection function composite flocculation agent and preparation method thereof
CN107999029A (en) A kind of coir fibre composite Nano ferriferous oxide heavy metal stabilizer and preparation method thereof

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
WW01 Invention patent application withdrawn after publication

Application publication date: 20160921

WW01 Invention patent application withdrawn after publication