CN109317508A - The vitrifying additive and its renovation technique of a kind of pair of heavy metal pollution soil remediation - Google Patents

The vitrifying additive and its renovation technique of a kind of pair of heavy metal pollution soil remediation Download PDF

Info

Publication number
CN109317508A
CN109317508A CN201811170375.7A CN201811170375A CN109317508A CN 109317508 A CN109317508 A CN 109317508A CN 201811170375 A CN201811170375 A CN 201811170375A CN 109317508 A CN109317508 A CN 109317508A
Authority
CN
China
Prior art keywords
additive
vitrifying
heavy metal
pair
heavy
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201811170375.7A
Other languages
Chinese (zh)
Inventor
朱华军
周嘉泰
马力
刘风学
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.)
Yao Zhejiang Green Ecological Environment Co Ltd
Original Assignee
Yao Zhejiang Green Ecological Environment 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 Yao Zhejiang Green Ecological Environment Co Ltd filed Critical Yao Zhejiang Green Ecological Environment Co Ltd
Priority to CN201811170375.7A priority Critical patent/CN109317508A/en
Publication of CN109317508A publication Critical patent/CN109317508A/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C1/00Reclamation of contaminated soil
    • B09C1/08Reclamation of contaminated soil chemically
    • CCHEMISTRY; METALLURGY
    • C09DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09KMATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
    • C09K17/00Soil-conditioning materials or soil-stabilising materials
    • C09K17/02Soil-conditioning materials or soil-stabilising materials containing inorganic compounds only
    • C09K17/06Calcium compounds, e.g. lime

Landscapes

  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Soil Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Inorganic Chemistry (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The invention belongs to technical field of soil remediation, more particularly to the vitrifying additive of a kind of pair of heavy metal pollution soil remediation, the vitrifying additive of the heavy-metal contaminated soil reparation includes silica 25%~40%, borax 2%~4%, calcium hydroxide 4%~6%, metal-chelator 3%~5%, sodium carbonate 4%~6%, magnesium sulfate 2%~4%, carbon 5%~7% and ferrous sulfate 1%~3% according to adding raw materials mass percent, remaining is water;Additive of the present invention is simple and is easy to get extensively, it is easy to industrialized production, with good economy and environmental benefit, heavy metal ion effect after high temp glassization reparation is extremely stable, and the soil sample after repairing can carry out recycling recycling, to increase economic efficiency, the soil sample after vitrifying is repaired, which can be sent to shipyard, to be carried out sandblasting or is directly transported to cement kiln to recycle as clinker.

Description

The vitrifying additive and its renovation technique of a kind of pair of heavy metal pollution soil remediation
Technical field
The invention belongs to technical field of soil remediation, and in particular to the vitrifying of a kind of pair of heavy metal pollution soil remediation adds Add agent and its renovation technique.
Background technique
With the development of the modernization of industry, soil pollution has become the principal element for endangering the national economic development, and The feature of soil pollution maximum is concealment, permanence and irreversibility, therefore is being badly in need of a kind of means at present to contaminated soil Administer effectively and for a long time.Vitrification is useless primarily directed to the high danger of inorganic content in existing disposal technology The recycling of object or contaminated soil, a kind of innoxious higher technology of level, therefore as this efficient disposal technology develops It is bound to realize domestic contaminated soil " zero-emission " this ambitious goal in the near future.
Summary of the invention
The purpose of the present invention is to provide a kind of vitrifying additive of efficient heavy contaminated soil remediation and its reparations Technique, to solve the problems mentioned in the above background technology.
To achieve the above object, the invention provides the following technical scheme: the glass of a kind of pair of heavy metal pollution soil remediation Change additive, the vitrifying additive of the heavy-metal contaminated soil reparation includes dioxy according to the mass percent of adding raw materials SiClx 25%~40%, borax 2%~4%, calcium hydroxide 4%~6%, metal-chelator 3%~5%, sodium carbonate 4%~ 6%, magnesium sulfate 2%~4%, carbon 5%~7% and ferrous sulfate 1%~3%.
Preferably, the vitrifying additive of the heavy-metal contaminated soil reparation according to adding raw materials mass percent also Including water 15%~25%.
The renovation technique of the vitrifying additive of a kind of pair of heavy metal pollution soil remediation, the heavy-metal contaminated soil are repaired The renovation technique of multiple vitrifying additive comprises the following steps:
S1, additive is prepared,
A, according to addition mass ratio choose silica 25%~40%, borax 2%~4%, calcium hydroxide 4%~6%, Metal-chelator 3%~5%, sodium carbonate 4%~6%, magnesium sulfate 2%~4%, carbon 5%~7%, ferrous sulfate 1%~ 3%, remaining is water;
B, the raw material chosen in a is sufficiently mixed by stirring and additive is made;
S2, raw material are chosen, and the bulk particulate matter of the additive and contaminated soil that prepare in S1 is chosen;
The bulk particulate matter of contaminated soil in S2 is screened, and is put into blender by S3, Raw material processing;
S4, reparation, the additive prepared in water and S1 is added into blender, and starting blender stirs certain time, makes Water and additive are sufficiently mixed with contaminated soil;
The material stirred evenly in S4 is put into disposition furnace and carries out vitrifying processing, to make material by S5, dry glass Dry glass;
S6, detection detect the content of heavy metal in cured product in S5 according to ad hoc approach.
Preferably, in S1, the silica, borax, calcium hydroxide, metal-chelator, sodium carbonate, magnesium sulfate, carbon The smart and described ferrous sulfate is powdered.
Preferably, in S1, the time of the additive preparation stirring is 5-10 minutes.
Preferably, in S4, the time of the blender stirring is 10-20 minutes.
Preferably, in S5, at 1050 DEG C~1350 DEG C, the processing time is the vitrified temperature control of the disposition furnace 35min~75min.
Preferably, in S6, the method for the detection is the measurement inductive coupling of 22 kinds of metallic elements of solid waste Plasma emlssion spectrometry HJ781-2016.
Additive of the present invention is simple and is easy to get extensively, easy to industrialized production, has good economy and environmental benefit, weight Metal ion repairing effect after high temp glass is extremely stable, and it is repaired after soil sample can to carry out recycling sharp again With to increase economic efficiency, the soil sample after vitrifying additive reparation can be sent to shipyard and carry out sandblasting or directly fortune It is recycled to cement kiln as clinker.
Specific embodiment
Below with reference to embodiment, the present invention will be further described.
The following examples are intended to illustrate the invention, but cannot be used to limit the scope of the invention.Item in embodiment Part can be adjusted according to actual conditions are further, under concept thereof of the invention all to method simple modifications of the invention Belong to the scope of protection of present invention.
Embodiment 1
The vitrifying additive of a kind of pair of heavy metal pollution soil remediation, the vitrifying of the heavy-metal contaminated soil reparation Additive according to the mass percent of adding raw materials include silica 25%~40%, borax 2%~4%, calcium carbonate 4%~ 6%, metal-chelator 3%~5%, calcium hydroxide 4%~6%, magnesium sulfate 2%~4%, carbon 5%~7% and ferrous sulfate 1%~3%, the vitrifying additive of the heavy-metal contaminated soil reparation further includes water according to the mass percent of adding raw materials 15%~25%.
The renovation technique of the vitrifying additive of a kind of pair of heavy metal pollution soil remediation, the heavy-metal contaminated soil are repaired The renovation technique of multiple vitrifying additive comprises the following steps:
S1, additive is prepared,
A, according to addition mass ratio choose silica 25%~40%, borax 2%~4%, calcium hydroxide 4%~6%, Metal-chelator 3%~5%, sodium carbonate 4%~6%, magnesium sulfate 2%~4%, carbon 5%~7% and ferrous sulfate 1%~ 3%, remaining is water, the silica, borax, calcium hydroxide 4%~6%, metal-chelator, sodium carbonate, magnesium sulfate, carbon It is powdered with the ferrous sulfate;
B, the raw material chosen in a is sufficiently mixed by stirring and additive is made, the time of the additive preparation stirring It is 5-10 minutes;
S2, raw material are chosen, and the bulk particulate matter of the additive and contaminated soil that prepare in S1 is chosen;
The bulk particulate matter of contaminated soil in S2 is screened, and is put into blender by S3, Raw material processing;
S4, reparation, the additive prepared in water and S1 is added into blender, and starting blender stirs 10-20 minutes, makes Water and additive are sufficiently mixed with contaminated soil;
The material stirred evenly in S4 is put into disposition furnace and carries out vitrifying processing, the disposition furnace by S5, dry glass Vitrified temperature control is at 1050 DEG C~1350 DEG C, and the processing time is 35min~75min, to make dry materials vitrifying;
S6, detection, according to the measurement inductively coupled plasma atomic emission of 22 kinds of metallic elements of solid waste Method HJ781-2016 detects the content of heavy metal in cured product in S5.
Embodiment 2
The vitrifying additive of a kind of pair of heavy metal pollution soil remediation, the vitrifying of the heavy-metal contaminated soil reparation Additive includes silica 25%~40%, borax 2%~4%, calcium hydroxide 4% according to the mass percent of adding raw materials ~6%, metal-chelator 3%~5%, sodium carbonate 4%~6%, magnesium sulfate 2%~4%, carbon 5%~7% and ferrous sulfate 1%~3%, the vitrifying additive of the heavy-metal contaminated soil reparation further includes water according to the mass percent of adding raw materials 15%~25%.
The renovation technique of the vitrifying additive of a kind of pair of heavy metal pollution soil remediation, the heavy-metal contaminated soil are repaired The renovation technique of multiple vitrifying additive comprises the following steps:
S1, additive is prepared,
A, according to addition mass ratio choose silica 25%~40%, borax 2%~4%, calcium hydroxide 4%~6%, Metal-chelator 3%~5%, sodium carbonate 4%~6%, magnesium sulfate 2%~4%, carbon 5%~7% and ferrous sulfate 1%~ 3%, remaining is water, the silica, borax, calcium hydroxide, metal-chelator, sodium carbonate, magnesium sulfate, carbon and the sulphur Sour ferrous iron is powdered;
B, the raw material chosen in a is sufficiently mixed by stirring and additive is made, the time of the additive preparation stirring It is 5 minutes;
S2, raw material are chosen, and the bulk particulate matter of the additive and contaminated soil that prepare in S1 is chosen;
The bulk particulate matter of contaminated soil in S2 is screened, and is put into blender by S3, Raw material processing;
The additive prepared in water and S1 is added into blender by S4, reparation, and starting blender stirs 20 minutes, makes water It is sufficiently mixed with additive and contaminated soil;
The material stirred evenly in S4 is put into disposition furnace and carries out vitrifying processing, the disposition furnace by S5, dry glass Vitrified temperature control is at 1050 DEG C~1350 DEG C, and the processing time is 35min~75min, to make dry materials vitrifying;
S6, detection, according to the measurement inductively coupled plasma atomic emission of 22 kinds of metallic elements of solid waste Method HJ781-2016 detects the content of heavy metal in cured product in S5.
Embodiment 3
The vitrifying additive of a kind of pair of heavy metal pollution soil remediation, the vitrifying of the heavy-metal contaminated soil reparation Additive includes silica 25%~40%, borax 2%~4%, calcium hydroxide 4% according to the mass percent that raw material adds ~6%, metal-chelator 3%~5%, sodium carbonate 4%~6%, magnesium sulfate 2%~4%, carbon 5%~7% and ferrous sulfate 1%~3%, the vitrifying additive of the heavy-metal contaminated soil reparation further includes water according to the mass percent that raw material adds 15%~25%.
The renovation technique of the vitrifying additive of a kind of pair of heavy metal pollution soil remediation, the heavy-metal contaminated soil are repaired The renovation technique of multiple vitrifying additive comprises the following steps:
S1, additive is prepared,
A, according to addition mass ratio choose silica 25%~40%, borax 2%~4%, calcium hydroxide 4%~6%, Metal-chelator 3%~5%, sodium carbonate 4%~6%, magnesium sulfate 2%~4%, carbon 5%~7% and ferrous sulfate 1%~ 3%, remaining is water, the silica, borax, calcium hydroxide, metal-chelator, sodium carbonate, magnesium sulfate, carbon and the sulphur Sour ferrous iron is powdered;
B, the raw material chosen in a is sufficiently mixed by stirring and additive is made, the time of the additive preparation stirring It is 10 minutes;
S2, raw material are chosen, and the bulk particulate matter of the additive and contaminated soil that prepare in S1 is chosen;
The bulk particulate matter of contaminated soil in S2 is screened, and is put into blender by S3, Raw material processing;
The additive prepared in water and S1 is added into blender by S4, reparation, and starting blender stirs 10 minutes, makes water It is sufficiently mixed with additive and contaminated soil;
The material stirred evenly in S4 is put into disposition furnace and carries out vitrifying processing, the disposition furnace by S5, dry glass Vitrified temperature control is at 1050 DEG C~1350 DEG C, and the processing time is 35min~75min, to make dry materials vitrifying;
S6, detection, according to the measurement inductively coupled plasma atomic emission of 22 kinds of metallic elements of solid waste Method HJ781-2016 detects the content of heavy metal in cured product in S5.
The concrete case repaired using this method to contaminated soil is as follows:
Case 1
Front and back Soil K+adsorption result (unit mg/L) is repaired in Hangzhou project vitrifying
Case 2
Table two: front and back Soil K+adsorption result (unit mg/L) is repaired in Shijiazhuang project vitrifying
Case 3
Three: front and back Soil K+adsorption result (unit mg/L) is repaired in Distributions in Liaocheng of Shandong Province vitrifying
Obtained according to the above concrete case: contaminated soil detects it after vitrification is handled, the side of detection Method uses the measurement inductively coupled plasma emission spectrography HJ781-2016 of 22 kinds of metallic elements of solid waste, Heavy-metal contaminated soil is evaluated after vitrifying is disposed, it is possible to find through vitrification, treated that soil sample all meets country The contaminated soil remediation standard and soil sample after repairing can carry out resource utilization, thus the vitrification be have it is stronger Practical value.
It although an embodiment of the present invention has been shown and described, for the ordinary skill in the art, can be with A variety of variations, modification, replacement can be carried out to these embodiments without departing from the principles and spirit of the present invention by understanding And modification, the scope of the present invention is defined by the appended.

Claims (8)

1. the vitrifying additive of a kind of pair of heavy metal pollution soil remediation, it is characterised in that: the heavy-metal contaminated soil is repaired Multiple vitrifying additive includes silica 25%~40%, borax 2%~4%, hydroxide according to adding raw materials mass percent Calcium 4%~6%, metal-chelator 3%~5%, sodium carbonate 4%~6%, magnesium sulfate 2%~4%, carbon 5%~7% and ferrous sulfate 1%~ 3%。
2. the vitrifying additive of a kind of pair of heavy metal pollution soil remediation according to claim 1, it is characterised in that: institute It further includes water 15%~25% that the vitrifying additive of heavy-metal contaminated soil reparation, which is stated, according to the mass percent of adding raw materials.
3. the renovation technique of the vitrifying additive of a kind of pair of heavy metal pollution soil remediation according to claim 2, Be characterized in that: the renovation technique of the vitrifying additive of the heavy-metal contaminated soil reparation comprises the following steps:
S1, additive is prepared;
A chooses silica 25%~40%, borax 2%~4%, calcium hydroxide 4%~6%, metal-chelator according to addition mass ratio 3%~5%, sodium carbonate 4%~6%, magnesium sulfate 2%~4%, carbon 5%~7% and ferrous sulfate 1%~3%, remaining is water;
The raw material chosen in a is sufficiently mixed by stirring, additive is made;
S2, raw material are chosen, and the bulk particulate matter of the additive and contaminated soil that prepare in S1 is chosen;
The bulk particulate matter of contaminated soil in S2 is screened, and is put into blender by S3, Raw material processing;
The additive prepared in water and S1 is added into blender by S4, reparation, and starting blender stirs certain time, make water and Additive is sufficiently mixed with contaminated soil;
The material stirred evenly in S4 is put into disposition furnace and carries out vitrifying processing, to make dry materials by S5, dry glass Vitrifying;
S6, detection detect the content of heavy metal in cured product in S5 according to ad hoc approach.
4. the renovation technique of the vitrifying additive of a kind of pair of heavy metal pollution soil remediation according to claim 3, It is characterized in that: in S1, the silica, borax, calcium hydroxide, metal-chelator, sodium carbonate, magnesium sulfate, carbon and institute It is powdered for stating ferrous sulfate.
5. the renovation technique of the vitrifying additive of a kind of pair of heavy metal pollution soil remediation according to claim 3, Be characterized in that: in S1, the time of the additive preparation stirring is 5-10 minutes.
6. the renovation technique of the vitrifying additive of a kind of pair of heavy metal pollution soil remediation according to claim 3, Be characterized in that: in S4, the time of the blender stirring is 10-20 minutes.
7. the renovation technique of the vitrifying additive of a kind of pair of heavy metal pollution soil remediation according to claim 3, Be characterized in that: in S5, the vitrified temperature control of the disposition furnace 1050 DEG C~1350, the processing time for 35min~ 75min。
8. the renovation technique of the vitrifying additive of a kind of pair of heavy metal pollution soil remediation according to claim 3, Be characterized in that: in S6, the method for the detection is the measurement inductively coupled plasma of 22 kinds of metallic elements of solid waste Body emission spectrometry HJ781-2016.
CN201811170375.7A 2018-10-09 2018-10-09 The vitrifying additive and its renovation technique of a kind of pair of heavy metal pollution soil remediation Pending CN109317508A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201811170375.7A CN109317508A (en) 2018-10-09 2018-10-09 The vitrifying additive and its renovation technique of a kind of pair of heavy metal pollution soil remediation

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201811170375.7A CN109317508A (en) 2018-10-09 2018-10-09 The vitrifying additive and its renovation technique of a kind of pair of heavy metal pollution soil remediation

Publications (1)

Publication Number Publication Date
CN109317508A true CN109317508A (en) 2019-02-12

Family

ID=65261050

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201811170375.7A Pending CN109317508A (en) 2018-10-09 2018-10-09 The vitrifying additive and its renovation technique of a kind of pair of heavy metal pollution soil remediation

Country Status (1)

Country Link
CN (1) CN109317508A (en)

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103586267A (en) * 2013-11-05 2014-02-19 南京农业大学 Method for immobilization of heavy metal in soil
CN105238409A (en) * 2015-11-04 2016-01-13 北京高能时代环境技术股份有限公司 Linkage stabilizing agent for repairing heavy metal contaminated soil and repairing method
CN105855276A (en) * 2015-01-22 2016-08-17 郭信麟 Treatment method for removing and stabilizing heavy metals in soil and repair agent
CN106244163A (en) * 2016-08-04 2016-12-21 北京高能时代环境技术股份有限公司 The reparation medicament of Compound Heavy Metals soil and methods for making and using same thereof

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103586267A (en) * 2013-11-05 2014-02-19 南京农业大学 Method for immobilization of heavy metal in soil
CN105855276A (en) * 2015-01-22 2016-08-17 郭信麟 Treatment method for removing and stabilizing heavy metals in soil and repair agent
CN105238409A (en) * 2015-11-04 2016-01-13 北京高能时代环境技术股份有限公司 Linkage stabilizing agent for repairing heavy metal contaminated soil and repairing method
CN106244163A (en) * 2016-08-04 2016-12-21 北京高能时代环境技术股份有限公司 The reparation medicament of Compound Heavy Metals soil and methods for making and using same thereof

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
德)康拉德•莱夫(KONRD REIF)主编;魏春源译: "《BOSCH 汽车工程手册》", 31 January 2016, 北京:北京理工大学出版社 *
李国建主编: "《固体废物处理与资源化工程》", 31 March 2001, 北京:高等教育出版社 *
王贝贝等: "重金属污染土壤微波玻璃化技术研究", 《环境工程》 *

Similar Documents

Publication Publication Date Title
Huang et al. Recent progress on the thermal treatment and resource utilization technologies of municipal waste incineration fly ash: A review
US20210323877A1 (en) Synergistic disposal method of hazardous waste incineration residues and solid wastes, ceramsite and application thereof
Lim et al. Recycling dredged harbor sediment to construction materials by sintering with steel slag and waste glass: Characteristics, alkali-silica reactivity and metals stability
CN104162533B (en) Harmless processing method of wastes containing heavy metals
CN106966621A (en) A kind of method that electroplating sludge prepares baking-free ceramicite
CN105712739B (en) Magnetic biological ceramsite prepared from waste incineration fly ash and preparation method thereof
Lv et al. Performance of ultra-high-performance concrete incorporating municipal solid waste incineration fly ash
CN105294142A (en) Red-mud-based sintered light aggregate and preparation method thereof
CN114292124A (en) Ceramsite fired by fly ash and preparation method and application thereof
Chen et al. Municipal solid waste incineration residues recycled for typical construction materials—A review
CN103145403B (en) Heavy metal stabilizing method in process of preparing filler by chemical sludge burning ash
CN101775868B (en) Method for sintering and curing industrial waste residue
CN107986726A (en) A kind of method that electrolytic manganese residues prepare high resistance to compression steam pressure pavior brick with ardealite
CN104310813A (en) Green ecological cement with stone wastes as raw material and production method of green ecological cement
CN113800941B (en) Method for preparing ceramsite by utilizing chromium-contaminated soil and ceramsite
CN111620647A (en) Cementing filler containing grate furnace garbage incineration fly ash and preparation method thereof
Pang et al. Review on the use of sludge in cement kilns: Mechanism, technical, and environmental evaluation
Huang et al. The effects of washing solvents on the properties of ceramsite and heavy metal immobilization via the cosintering of municipal solid waste incineration fly ash and Cr-containing waste glass
CN111559878A (en) Cementing filler containing fluidized bed waste incineration fly ash and preparation method thereof
CN109317508A (en) The vitrifying additive and its renovation technique of a kind of pair of heavy metal pollution soil remediation
He et al. Effects and mechanism of the conditions of sintering on heavy metal leaching characteristic in municipal solid waste incineration fly ash
CN116655266A (en) Low-cost clinker-free cementing material and application thereof
JP2007275868A (en) Calcined product manufacturing method
AU2021106088A4 (en) Preparation Method and Application of Low-Cost Clinker-free Cementitious backfill Materials
CN108609877A (en) Cure the method that landfill body prepares clinker using shale gas drilling well solid waste

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20190212

RJ01 Rejection of invention patent application after publication