CN109570183A - A kind of method of arsenic-containing waste residue solidification and stabilization processing - Google Patents
A kind of method of arsenic-containing waste residue solidification and stabilization processing Download PDFInfo
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- CN109570183A CN109570183A CN201811186022.6A CN201811186022A CN109570183A CN 109570183 A CN109570183 A CN 109570183A CN 201811186022 A CN201811186022 A CN 201811186022A CN 109570183 A CN109570183 A CN 109570183A
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- Prior art keywords
- arsenic
- solidification
- waste residue
- containing waste
- stabilization
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Links
- 229910052785 arsenic Inorganic materials 0.000 title claims abstract description 66
- RQNWIZPPADIBDY-UHFFFAOYSA-N arsenic atom Chemical compound [As] RQNWIZPPADIBDY-UHFFFAOYSA-N 0.000 title claims abstract description 64
- 238000007711 solidification Methods 0.000 title claims abstract description 56
- 230000008023 solidification Effects 0.000 title claims abstract description 56
- 239000002699 waste material Substances 0.000 title claims abstract description 53
- 230000006641 stabilisation Effects 0.000 title claims abstract description 45
- 238000011105 stabilization Methods 0.000 title claims abstract description 45
- 238000000034 method Methods 0.000 title claims abstract description 37
- 238000012545 processing Methods 0.000 title claims abstract description 20
- 239000004568 cement Substances 0.000 claims abstract description 37
- 239000003381 stabilizer Substances 0.000 claims abstract description 18
- 238000009412 basement excavation Methods 0.000 claims abstract description 10
- 238000012216 screening Methods 0.000 claims abstract description 10
- 238000002386 leaching Methods 0.000 claims abstract description 8
- 238000005259 measurement Methods 0.000 claims abstract description 7
- 239000004745 nonwoven fabric Substances 0.000 claims description 20
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 14
- 229920001903 high density polyethylene Polymers 0.000 claims description 13
- 239000004700 high-density polyethylene Substances 0.000 claims description 13
- 230000002209 hydrophobic effect Effects 0.000 claims description 13
- 239000003814 drug Substances 0.000 claims description 9
- 239000002689 soil Substances 0.000 claims description 9
- 238000001723 curing Methods 0.000 claims description 8
- 239000011248 coating agent Substances 0.000 claims description 6
- 238000000576 coating method Methods 0.000 claims description 6
- 230000006835 compression Effects 0.000 claims description 6
- 238000007906 compression Methods 0.000 claims description 6
- 238000002156 mixing Methods 0.000 claims description 5
- 239000011435 rock Substances 0.000 claims description 4
- 239000002893 slag Substances 0.000 claims description 4
- 230000000087 stabilizing effect Effects 0.000 claims description 4
- 238000007599 discharging Methods 0.000 claims description 3
- 238000000465 moulding Methods 0.000 claims description 3
- 239000002351 wastewater Substances 0.000 claims description 3
- 102000002322 Egg Proteins Human genes 0.000 claims 1
- 108010000912 Egg Proteins Proteins 0.000 claims 1
- 239000003795 chemical substances by application Substances 0.000 claims 1
- 210000004681 ovum Anatomy 0.000 claims 1
- 239000004575 stone Substances 0.000 claims 1
- 238000005516 engineering process Methods 0.000 abstract description 8
- 238000003672 processing method Methods 0.000 abstract description 4
- 238000006703 hydration reaction Methods 0.000 abstract description 2
- 229910010272 inorganic material Inorganic materials 0.000 abstract description 2
- 239000011147 inorganic material Substances 0.000 abstract description 2
- 239000000463 material Substances 0.000 abstract description 2
- 239000002910 solid waste Substances 0.000 abstract description 2
- 241000196324 Embryophyta Species 0.000 description 5
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 4
- 238000011084 recovery Methods 0.000 description 4
- 238000012544 monitoring process Methods 0.000 description 3
- 230000000694 effects Effects 0.000 description 2
- 239000004744 fabric Substances 0.000 description 2
- 229910052742 iron Inorganic materials 0.000 description 2
- 230000003014 reinforcing effect Effects 0.000 description 2
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 239000010426 asphalt Substances 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000011156 evaluation Methods 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 239000000376 reactant Substances 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 229920001169 thermoplastic Polymers 0.000 description 1
- 239000004416 thermosoftening plastic Substances 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G22/00—Cultivation of specific crops or plants not otherwise provided for
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G24/00—Growth substrates; Culture media; Apparatus or methods therefor
- A01G24/40—Growth substrates; Culture media; Apparatus or methods therefor characterised by their structure
- A01G24/44—Growth substrates; Culture media; Apparatus or methods therefor characterised by their structure in block, mat or sheet form
- A01G24/46—Growth substrates; Culture media; Apparatus or methods therefor characterised by their structure in block, mat or sheet form multi-layered
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B5/00—Operations not covered by a single other subclass or by a single other group in this subclass
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Environmental Sciences (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Botany (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
The invention belongs to field of solid waste treating technology, and in particular to a kind of method of arsenic-containing waste residue solidification and stabilization processing.A kind of method of arsenic-containing waste residue solidification and stabilization processing includes excavation of earthwork, crushing and screening, solidification and stabilization, stockpiling measurement, landfill and etc..Arsenic-containing waste residue is handled using method of the invention, since cement is a kind of cement inorganic material, hard solidified cement body can be generated after hydration reaction, leached to achieve the purpose that reduce hazard component in waste, be the most economic and material benefit method in solidification processing method.The cement block stability obtained after being handled by this method is good, and the leaching rate of arsenic is low, and solidification is easy to get and low in cost with stabilizer.
Description
Technical field
The invention belongs to field of solid waste treating technology, and in particular to a kind of processing of arsenic-containing waste residue solidification and stabilization
Method.
Background technique
Currently, the processing method to arsenic-containing waste residue is varied, wherein most commonly seen with curing/stabilizing technology.And consolidate
Change/stabilization technology is divided into following several according to the difference of the principle of solidification, and cement based stabilization/curing method, lime base are stablized
Change/solidification method, asphalt stabilization/curing method, thermoplastic stabilization/curing, glass stabilization/curing method and chemical stabilization
Technology.
Solidification and stabilization technology is the main recovery technique in China's contaminated site especially heavy metal pollution class place, however
China is unified not yet and explicitly evaluates the method and standard of solidification and stabilization repairing effect, also lacks solidification and stabilization product
Final disposal or the management regulation for recycling mode, therefore the stability of arsenic slag is to determine that its recovery project is real after solidification and stabilization
Principal element occurs for secondary pollution during applying.
Practiced according to developed country's solidification and stabilization recovery project: its most of solidification and stabilization is repaired place and is grown
Phase tracking and monitoring is attached most importance to groundwater environment safety monitoring, and the monitoring data table that history is up to more than 20 years places is repaired in part
Bright, the long-range circumstances safety of solidification and stabilization technology is fine, substantially not there is a phenomenon where being more than expected standard, and partially refers to
Mark the trend for having showed and significantly having improved at any time.
In recent years, the recovery technique being most widely used in the reparation of China's contaminated site is solidification and stabilization, in addition China
There has been no the methods and standard of unified and specific evaluation solidification and stabilization repairing effect, therefore many scholars also just stablize by solidification
The stability of change has carried out experimental study.But there has been no the solidification and stabilizations that a whole set of can be wide, perfect with applicability at present
Processing system and processing method.
Summary of the invention
It is an object of the present invention to solve the deficiency of the existing technology and provide a kind of processing of arsenic-containing waste residue solidification and stabilization
Method.
The present invention is achieved by the following technical solution:
A kind of method of arsenic-containing waste residue solidification and stabilization processing, comprises the following steps,
(1) excavation of earthwork, the earth excavation by the way of mechanical excavation, average cutting depth is 2.5m, obtains arsenic-containing waste residue, opens
Using the concentration of arsenic in Portable X RF on-site measurement soil during digging, the arsenic-containing waste residue excavated out is transported using airtight transportation vehicle
It is defeated；The ponding occurred in digging process is evacuated to arsenic-containing waste water collecting pit with water pump, is transported at landfill yard water treatment system
Reason；Control moisture content≤25% of arsenic-containing waste residue；
(2) crushing and screening, using movable Crushing screening process device, so that the partial size < 10mm of obtained arsenic-containing waste residue, and
The sundries that equipment runs well is influenced without containing cloth waste, iron wire, reinforcing bar, branch, weeds etc.；
(3) solidification and stabilization, the arsenic-containing waste residue obtained afterwards after crushing and screening are sent into feeding warehouse by belt conveyor, then percutaneously
Band transporter is sent into mobile solidification stabilization system and equipment is mixed, and is proportionally added into cement and solidification stabilizer, passes through
Cement block is obtained after block machine molding, between cement block send the waste in curing/stabilizing workshop temporary after metering；Control water
The moisture content of clod is 30%；
(4) stockpiling measurement measures its compression strength, contains after the solidification and stabilization cement block that treated obtains places 7-10 d
The content of water rate and leaching arsenic；When the result measured is compression strength >=0.5MPa, moisture content is 30% ± 2%, leaching arsenic
When content≤2.5mg/L, into landfill operation, otherwise return step (2) is handled again；
(5) it fills, the cement block that will be provided with landfill condition is transported to landfill yard and carries out security landfill disposition, is equipped with and covers above buring layer
Cap rock, coating depth > 1.3m.
Cement passes through quantitative discharging device and screw conveyor feeding mixing equipment under cement bunker.
Solidification is delivered to mixing equipment by metering pump from make-up tank with stabilizer.
Preferably, the cement consumption of arsenic-containing waste residue per ton is 30kg, the dosage of arsenic-containing waste residue per ton solidified with stabilizer
For 30L.
The solidification is the solidification proprietary medicament that stabilizer is that engineering proportion is 3% with stabilizer, described
Proprietary medicament is ion mineralising stabilizer GF206 medicament.
Preferably, the belt conveyor is closed belt conveyor.
Preferably, the arsenic-containing waste residue includes the slag containing arsenic and the soil crossed by arsenic pollution.
The coating is followed successively by back fill course, cobble hydrophobic layer and HDPE antiseepage film layer from top to bottom, and described returns
The thickness G T.GT.GT 1m of fill stratum, kind is implanted with plant on back fill course；The cobble hydrophobic layer with a thickness of 0.3m, cobble hydrophobic layer
Geotechnological non-woven fabrics 1 is equipped between back fill course；The HDPE antiseepage film layer is the smooth surface HDPE geomembrane with a thickness of 1mm,
Geotechnological non-woven fabrics 2 is equipped between HDPE antiseepage film layer and cobble hydrophobic layer.
The geotechnological non-woven fabrics 1 is 300g/m2Geotechnological non-woven fabrics, the geotechnological non-woven fabrics 2 be 600g/m2Soil
Work non-woven fabrics.
Compared with prior art, the invention has the following beneficial effects: the present invention provides a kind of using cement to containing arsenic
The method of residue stabilization stabilization processes can directly be neutralized, cement solidification because cement is alkaline matter with spent acid class waste
When need to use water and make reactant, so the waste bigger to water content is also suitable.Arsenic is contained using method processing of the invention
Since cement is a kind of cement inorganic material hard solidified cement body can be generated, to reach in waste residue after hydration reaction
It is the most economic and material benefit method in solidification processing method to the purpose that hazard component leaches in waste is reduced.Pass through we
Obtained cement block stability is good after method processing, and the leaching rate of arsenic is low, and solidification is easy to get and low in cost with stabilizer.
Detailed description of the invention
Fig. 1 is the structural schematic diagram of coating of the invention；
In figure: 1- plant, 2- back fill course, 3- geotechnique's non-woven fabrics Isosorbide-5-Nitrae-cobble hydrophobic layer, 5- geotechnique's non-woven fabrics 2,6-HDPE are anti-
Seep film layer, 7- cement block.
Specific embodiment
Below with reference to embodiment, the present invention will be further described, but protection scope of the present invention is not limited by embodiment
System.
Embodiment 1
A kind of method of arsenic-containing waste residue solidification and stabilization processing, comprises the following steps,
(1) excavation of earthwork, the earth excavation by the way of mechanical excavation, average cutting depth is 2.5m, obtains arsenic-containing waste residue, opens
Using the concentration of arsenic in Portable X RF on-site measurement soil during digging, the arsenic-containing waste residue excavated out is transported using airtight transportation vehicle
It is defeated；The ponding occurred in digging process is evacuated to arsenic-containing waste water collecting pit with water pump, is transported at landfill yard water treatment system
Reason；Control moisture content≤25% of arsenic-containing waste residue；
(2) crushing and screening, using movable Crushing screening process device, so that the partial size < 10mm of obtained arsenic-containing waste residue, and
The sundries that equipment runs well is influenced without containing cloth waste, iron wire, reinforcing bar, branch, weeds etc.；
(3) solidification and stabilization, the arsenic-containing waste residue obtained afterwards after crushing and screening are sent into feeding warehouse by belt conveyor, then percutaneously
Band transporter is sent into mobile solidification stabilization system and equipment is mixed, and is proportionally added into cement and solidification stabilizer, passes through
Cement block is obtained after block machine molding, between cement block send the waste in curing/stabilizing workshop temporary after metering；Control water
The moisture content of clod is 30%；
(4) stockpiling measurement measures its compression strength, contains after the solidification and stabilization cement block that treated obtains places 7-10 d
The content of water rate and leaching arsenic；When the result measured is compression strength >=0.5MPa, moisture content is 30% ± 2%, leaching arsenic
When content≤2.5mg/L, into landfill operation, otherwise return step (2) is handled again；
(5) it fills, the cement block that will be provided with landfill condition is transported to landfill yard and carries out security landfill disposition, is equipped with and covers above buring layer
Cap rock, coating depth > 1.3m.
Cement passes through quantitative discharging device and screw conveyor feeding mixing equipment under cement bunker.
Solidification is delivered to mixing equipment by metering pump from make-up tank with stabilizer.
Preferably, the cement consumption of arsenic-containing waste residue per ton is 30kg, the dosage of arsenic-containing waste residue per ton solidified with stabilizer
For 30L.
The solidification is the solidification proprietary medicament that stabilizer is that engineering proportion is 3% with stabilizer, described
Proprietary medicament is ion mineralising stabilizer GF206 medicament.
Preferably, the belt conveyor is closed belt conveyor.
Preferably, the arsenic-containing waste residue includes the slag containing arsenic and the soil crossed by arsenic pollution.
The coating is followed successively by back fill course, cobble hydrophobic layer and HDPE antiseepage film layer from top to bottom, and described returns
The thickness G T.GT.GT 1m of fill stratum, kind is implanted with plant on back fill course；The cobble hydrophobic layer with a thickness of 0.3m, cobble hydrophobic layer
Geotechnological non-woven fabrics 1 is equipped between back fill course；The HDPE antiseepage film layer is the smooth surface HDPE geomembrane with a thickness of 1mm,
Geotechnological non-woven fabrics 2 is equipped between HDPE antiseepage film layer and cobble hydrophobic layer.
The geotechnological non-woven fabrics 1 is 300g/m2Geotechnological non-woven fabrics, the geotechnological non-woven fabrics 2 be 600g/m2Soil
Work non-woven fabrics.
Claims (9)
1. a kind of method of arsenic-containing waste residue solidification and stabilization processing, which is characterized in that it comprises the following steps,
(1) excavation of earthwork, the earth excavation by the way of mechanical excavation, average cutting depth is 2.5m, obtains arsenic-containing waste residue, opens
Using the concentration of arsenic in Portable X RF on-site measurement soil during digging, the arsenic-containing waste residue excavated out is transported using airtight transportation vehicle
It is defeated；The ponding occurred in digging process is evacuated to arsenic-containing waste water collecting pit with water pump, is transported at landfill yard water treatment system
Reason；Control moisture content≤25% of arsenic-containing waste residue；
(2) crushing and screening, using movable Crushing screening process device, so that the partial size < 10mm of obtained arsenic-containing waste residue；
(3) solidification and stabilization, the arsenic-containing waste residue obtained afterwards after crushing and screening are sent into feeding warehouse by belt conveyor, then percutaneously
Band transporter is sent into mobile solidification stabilization system and equipment is mixed, and is proportionally added into cement and solidification stabilizer, passes through
Cement block is obtained after block machine molding, between cement block send the waste in curing/stabilizing workshop temporary after metering；Control water
The moisture content of clod is 30%；
(4) stockpiling measurement measures its compression strength, contains after the solidification and stabilization cement block that treated obtains places 7-10 d
The content of water rate and leaching arsenic；When the result measured is compression strength >=0.5MPa, moisture content is 30% ± 2%, leaching arsenic
When content≤2.5mg/L, into landfill operation, otherwise return step (2) is handled again；
(5) it fills, the cement block that will be provided with landfill condition is transported to landfill yard and carries out security landfill disposition, is equipped with and covers above buring layer
Cap rock, coating depth > 1.3m.
2. a kind of method of arsenic-containing waste residue solidification and stabilization processing according to claim 1, which is characterized in that cement passes through
Quantitative discharging device and screw conveyor under cement bunker, which are sent into, is mixed equipment.
3. a kind of method of arsenic-containing waste residue solidification and stabilization processing according to claim 1, which is characterized in that solidification is with surely
Determine agent and mixing equipment is delivered to by metering pump from make-up tank.
4. a kind of method of arsenic-containing waste residue solidification and stabilization processing according to claim 1, which is characterized in that per ton to contain arsenic
The cement consumption of waste residue is 30kg, and the dosage of the solidification stabilizer of arsenic-containing waste residue per ton is 30L.
5. a kind of method of arsenic-containing waste residue solidification and stabilization processing according to claim 1, which is characterized in that described consolidates
Change is ion mineralising stabilizer GF206 medicament with the proprietary medicament that stabilizer is that engineering proportion is 3%, the proprietary medicament.
6. a kind of method of arsenic-containing waste residue solidification and stabilization processing according to claim 1, which is characterized in that the skin
Band conveyer is closed belt conveyor.
7. a kind of method of arsenic-containing waste residue solidification and stabilization processing according to claim 1, which is characterized in that described contains
Arsenic waste residue includes the slag containing arsenic and the soil crossed by arsenic pollution.
8. a kind of method of arsenic-containing waste residue solidification and stabilization processing according to claim 1, which is characterized in that described covers
Cap rock is followed successively by back fill course, cobble hydrophobic layer and HDPE antiseepage film layer from top to bottom, the thickness G T.GT.GT 1m of the back fill course,
Kind is implanted with plant on back fill course；The cobble hydrophobic layer with a thickness of 0.3m, set between cobble hydrophobic layer and back fill course
There is geotechnological non-woven fabrics 1；The HDPE antiseepage film layer is the smooth surface HDPE geomembrane with a thickness of 1mm, HDPE antiseepage film layer and ovum
Geotechnological non-woven fabrics 2 is equipped between stone hydrophobic layer.
9. a kind of method of arsenic-containing waste residue solidification and stabilization processing according to claim 8, which is characterized in that the soil
Work non-woven fabrics 1 is 300g/m2Geotechnological non-woven fabrics, the geotechnological non-woven fabrics 2 be 600g/m2Geotechnological non-woven fabrics.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201811186022.6A CN109570183A (en) | 2018-10-12 | 2018-10-12 | A kind of method of arsenic-containing waste residue solidification and stabilization processing |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201811186022.6A CN109570183A (en) | 2018-10-12 | 2018-10-12 | A kind of method of arsenic-containing waste residue solidification and stabilization processing |
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| Publication Number | Publication Date |
|---|---|
| CN109570183A true CN109570183A (en) | 2019-04-05 |
Family
ID=65920327
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
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| CN201811186022.6A Pending CN109570183A (en) | 2018-10-12 | 2018-10-12 | A kind of method of arsenic-containing waste residue solidification and stabilization processing |
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| Country | Link |
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Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN111266402A (en) * | 2020-02-20 | 2020-06-12 | 北京市环境保护科学研究院 | Biological barrier system and method for blocking path of benzene series in field to move to atmosphere |
| CN113716925A (en) * | 2021-08-02 | 2021-11-30 | 上海市政工程设计研究总院（集团）有限公司 | Method for solidifying and stabilizing heavy metal arsenic in tailings and/or slag |
| CN115093168A (en) * | 2022-06-23 | 2022-09-23 | 昆明理工大学 | Method for fixing arsenic in tin tailings by using cement |
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE3343422A1 (en) * | 1983-12-01 | 1985-06-20 | Kernforschungsanlage Jülich GmbH, 5170 Jülich | METHOD FOR CONDITIONING CONTAMINATED WASTE BY CEMENTING |
| JP4130762B2 (en) * | 2002-11-05 | 2008-08-06 | Ｊｆｅミネラル株式会社 | Heavy metal stabilization treatment method |
| CN204657080U (en) * | 2015-04-13 | 2015-09-23 | 湖南艾布鲁环保科技有限公司 | Arsenic slag safe disposal system |
| CN204672683U (en) * | 2015-05-29 | 2015-09-30 | 湖南艾布鲁环保科技有限公司 | A kind of arsenic slag solidification process integrated system |
| CN107789787A (en) * | 2017-09-22 | 2018-03-13 | 广西壮族自治区环境监测中心站 | For repairing the stabilization agent and application method of arsenic-containing waste residue |
-
2018
- 2018-10-12 CN CN201811186022.6A patent/CN109570183A/en active Pending
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE3343422A1 (en) * | 1983-12-01 | 1985-06-20 | Kernforschungsanlage Jülich GmbH, 5170 Jülich | METHOD FOR CONDITIONING CONTAMINATED WASTE BY CEMENTING |
| JP4130762B2 (en) * | 2002-11-05 | 2008-08-06 | Ｊｆｅミネラル株式会社 | Heavy metal stabilization treatment method |
| CN204657080U (en) * | 2015-04-13 | 2015-09-23 | 湖南艾布鲁环保科技有限公司 | Arsenic slag safe disposal system |
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| CN107789787A (en) * | 2017-09-22 | 2018-03-13 | 广西壮族自治区环境监测中心站 | For repairing the stabilization agent and application method of arsenic-containing waste residue |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN111266402A (en) * | 2020-02-20 | 2020-06-12 | 北京市环境保护科学研究院 | Biological barrier system and method for blocking path of benzene series in field to move to atmosphere |
| CN113716925A (en) * | 2021-08-02 | 2021-11-30 | 上海市政工程设计研究总院（集团）有限公司 | Method for solidifying and stabilizing heavy metal arsenic in tailings and/or slag |
| CN115093168A (en) * | 2022-06-23 | 2022-09-23 | 昆明理工大学 | Method for fixing arsenic in tin tailings by using cement |
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