CN106001081A - Novel Sb in-situ detoxifying method for contaminated site based on biogas residues - Google Patents
Novel Sb in-situ detoxifying method for contaminated site based on biogas residues Download PDFInfo
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- CN106001081A CN106001081A CN201610370401.5A CN201610370401A CN106001081A CN 106001081 A CN106001081 A CN 106001081A CN 201610370401 A CN201610370401 A CN 201610370401A CN 106001081 A CN106001081 A CN 106001081A
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- sulfate
- biogas residue
- contaminated site
- medicament
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/02—Extraction using liquids, e.g. washing, leaching, flotation
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/08—Reclamation of contaminated soil chemically
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/10—Reclamation of contaminated soil microbiologically, biologically or by using enzymes
- B09C1/105—Reclamation of contaminated soil microbiologically, biologically or by using enzymes using fungi or plants
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C2101/00—In situ
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- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Soil Sciences (AREA)
- Mycology (AREA)
- Biotechnology (AREA)
- Biomedical Technology (AREA)
- General Health & Medical Sciences (AREA)
- Microbiology (AREA)
- Molecular Biology (AREA)
- Health & Medical Sciences (AREA)
- Botany (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
The invention discloses a novel Sb in-situ detoxifying method for a contaminated site based on biogas residues. The biogas residues, a carbon source and sulfate are prepared into a reagent to be injected into Sb-containing soil in an in-situ manner; and then a special construction and curing manner is adopted for a fixation biological bactericide to gradually permeate into the ground, and Sb of the contaminated soil on the deep layer is fixed. By means of the method, the Sb-containing site which is high in contamination depth can be efficiently repaired with low cost, meanwhile, waste is used for treating waste, and the biogas residues are treated.
Description
Technical field
The present invention provides a kind of method of novel process Sb contaminated soil; it is primarily directed to the soil that Sb pollution depth is higher; biogas residue, carbon source and sulfate are configured to medicament and are injected into containing in Sb soil in situ; use special maintenance method subsequently; Sb can be fixed efficiently; the most cost-effective, belong to field of environment protection.
Background technology
Owing to mining, Metallurgical Waste Water arbitrarily discharge, cause a large amount of soil and polluted by Sb.Process the method containing Sb soil at present the most defective.High-temperature melting method cost is high, and power consumption is big.Bioanalysis is long for reaction time, and easily causes the secondary pollution of adventive microbial inoculum.Solidification method effect is unstable, and soil is easily caused secondary pollution by firming agent.The patent No. 201510056406.6 describes a kind of curing containing heavy metal soil, but the method using substantial amounts of material, relatively costly, on the other hand solidification effect is unstable, the most easily there is carbonation in the calcium oxide as added so that alkaline-curing effect reduces.
Summary of the invention
For the deficiencies in the prior art, the present invention uses a kind of novel contaminated site Sb situ detoxification method based on biogas residue, biogas residue, carbon source and sulfate are configured to medicament and are injected into containing in Sb soil in situ, use special construction and maintenance method subsequently, make fixing ecological microbial agent gradually permeate the ground, deep layer polluted soil Sb is fixed.The place containing Sb that pollution depth is higher can be repaired by this method with low cost and efficiently, and biogas residue is processed by the treatment of wastes with processes of wastes against one another simultaneously.It comprises the steps of
(1) sodium sulfate, biogas residue or carbon source solution are mixed according to a certain percentage, after making mixing, solution dried biogas residues content is 0.1-20%, solid content 0.5-25%, organic carbon content 0.5-25%, the mass ratio of sulfate (remembering with SO4)/organic carbon is for (0-1): 1, mixed solution reaction 0-5 days, it is thus achieved that Sb soil remediation medicament;
(2) being forced through the reparation medicament batch (-type) in step (1) containing in Sb soil, injection pressure is at 0.1-1Mpa, and average every day, every square metre of injection rate was at 3-50 cube, was continued until that reparation terminates, during can constantly extract subsoil water;
(3) during repairing, it is desirable to the annual average rainfall in place is at more than 200mm, not enough then use the mode of surface sprinkling water to supplement, and enables medicament continuous to lower floor's seepage flow.
This method injects additional special field construction and maintenance in situ by special ecological medicament, place is promoted to form the flora based on sulfate reducting bacteria on a large scale, first this flora can utilize carbon source effectively to fix Sb, make full use of sulfate simultaneously, it is translated into sulfide, Sb simultaneously, is converted into more stable sulfuration Sb precipitation by the most fixing Sb.
Comparing traditional containing Sb agent, soil treatment method, this method has a following advantage:
1. the sulfate reducting bacteria sulphate reducing in biogas residue microbial inoculum, generates sulfide, can be while more efficient fixing Sb;
2. the sulfate reduction flora cultivated itself is indigenous flora, and natural tolerance is strong, easily multiplies on a large scale in place, can the most effectively fix Sb, and does not results in ecological problem;
3.Sb and sulfate reducting bacteria metabolite sulfide form sulfuration Sb precipitation so that in soil, Sb is more stable, is significantly better than other biochemical process;
4. this method uses biogas residue and debirs as primary raw material, greatly reduces cost;
5. this method uses in-situ immobilization to deep soil, it is to avoid the excavation of deep soil, greatly reduces cost.
It is embodied as example as follows:
Embodiment 1:
(1) sodium sulfate, biogas residue or carbon source solution are mixed according to a certain percentage, after making mixing, solution dried biogas residues content is 0.1-5%, solid content 0.5-5%, organic carbon content 0.5-5%, the mass ratio of sulfate (remembering with SO4)/organic carbon is as 0.1:1, mixed solution reaction 1 day, it is thus achieved that Sb soil remediation medicament;
(2) being forced through by the reparation medicament batch (-type) in step (1) containing in Sb soil, injection pressure is at 0.1-0.5Mpa, and average every day, every square metre of injection rate was at 50 cubes, was continued until that reparation terminates;
(3) during repairing, it is desirable to the annual average rainfall in place is at more than 200mm, not enough then use the mode of surface sprinkling water to supplement, and enables medicament continuous to lower floor's seepage flow;After engineering construction 2 years, more than 20 meters soil Sb stripping quantities of deep layer are below 2mg/kg, and subsoil water amount containing Sb is less than 0.1mg/L.
Embodiment 2:
(1) sodium sulfate, biogas residue or carbon source solution are mixed according to a certain percentage, after making mixing, solution dried biogas residues content is 5-20%, solid content 5-25%, organic carbon content 5-25%, the mass ratio of sulfate (remembering with SO4)/organic carbon is as 0.5:1, mixed solution reaction 2 days, it is thus achieved that Sb soil remediation medicament;
(2) being forced through the reparation medicament batch (-type) in step (1) containing in Sb soil, injection pressure is at 0.5-1Mpa, and average every day, every square metre of injection rate was at 10-20 cube, was continued until that reparation terminates;
(3) during repairing, it is desirable to the annual average rainfall in place is at more than 200mm, not enough then use the mode of surface sprinkling water to supplement, and enables medicament continuous to lower floor's seepage flow;After engineering construction 1 year, more than 40 meters soil Sb stripping quantities of deep layer are below 2mg/kg, and subsoil water amount containing Sb is less than 0.1mg/L.
Above example is only in order to illustrate technical scheme, rather than is limited;Although the present invention being described in detail with reference to previous embodiment, for the person of ordinary skill of the art, still the technical scheme described in previous embodiment can be modified, or wherein portion of techniques feature is carried out equivalent;And these amendments or replacement, do not make the essence of appropriate technical solution depart from the spirit and scope of claimed technical solution of the invention.
Claims (6)
1. a novel contaminated site Sb situ detoxification method based on biogas residue, is characterized in that, comprise the steps of
(1) sodium sulfate, biogas residue or carbon source solution are mixed according to a certain percentage, after making mixing, solution dried biogas residues content is 0.1-20%, solid content 0.5-25%, organic carbon content 0.5-25%, the mass ratio of sulfate (remembering with SO4)/organic carbon is for (0-1): 1, mixed solution reaction 0-5 days, it is thus achieved that Sb soil remediation medicament;
(2) being forced through the reparation medicament batch (-type) in step (1) containing in Sb soil, injection pressure is at 0.1-1Mpa, and average every day, every square metre of injection rate was at 3-50 cube, was continued until that reparation terminates;
(3) during repairing, it is desirable to the annual average rainfall in place is at more than 200mm, not enough then use the mode of surface sprinkling water to supplement, and enables medicament continuous to lower floor's seepage flow.
A kind of novel contaminated site Sb situ detoxification method based on biogas residue, is characterized in that, described biogas residue be agricultural, grocery trade debirs carry out the solid residue in dry type, half dry type and wet type anaerobic fermentation process.
A kind of novel contaminated site Sb situ detoxification method based on biogas residue, it is characterized in that, described carbon source solution can be containing organic solution such as ethanol, saccharide, protein, starch, can also be for the solution containing the industry organic solid waste such as organic waste, changing food waste, can also be industrial and municipal organic wastewater, described sodium sulfate can be substituted by the material of other containing sulfate.
A kind of novel contaminated site Sb situ detoxification method based on biogas residue, is characterized in that, constantly extracts subsoil water when of injecting medicament, forms negative pressure, makes medicament easily flow into underground.
A kind of novel contaminated site Sb situ detoxification method based on biogas residue, it is characterized in that, during reparation, the reparation medicament injecting place can be substituted by carbon source and sulfate mixed liquor, and in mixed liquor, the mass ratio of sulfate (remembering with SO4)/organic carbon is for (0-1): 1.
A kind of novel contaminated site Sb situ detoxification method based on biogas residue, it is characterized in that, carbon source and sulfate mixed liquor can add the subsoil water of place extracting, it is then injected in place, it is (0-1) that mixed liquid meets the mass ratio of Sb/ organic carbon: 1, and the mass ratio of sulfate (remembering with SO4)/organic carbon is for (0-1): 1.
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Citations (11)
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CN102873086A (en) * | 2012-10-09 | 2013-01-16 | 北京大学 | Mercury contaminated soil in-situ restoration method |
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CN103981875A (en) * | 2013-12-05 | 2014-08-13 | 青岛理工大学 | Landfill method capable of synchronously stabilizing chromium slag and household garbage |
CN103981097A (en) * | 2013-12-05 | 2014-08-13 | 青岛理工大学 | Preparation method of remediation flora for Cr (VI) contaminated site from sludge |
CN103978025A (en) * | 2013-12-05 | 2014-08-13 | 青岛理工大学 | Landfill method for rapid stabilization of chromium-containing soil and household garbage |
CN104275347A (en) * | 2014-10-22 | 2015-01-14 | 天津生态城环保有限公司 | Medicament injection device for in-situ remediation of pollution site |
CN105344705A (en) * | 2015-11-27 | 2016-02-24 | 上海岩土工程勘察设计研究院有限公司 | Injection device for in-situ remediation of contaminated sites |
CN105414163A (en) * | 2015-11-09 | 2016-03-23 | 四川龙蟒钛业股份有限公司 | Method for repairing cadmium contaminated soil |
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2016
- 2016-05-30 CN CN201610370401.5A patent/CN106001081A/en active Pending
Patent Citations (11)
Publication number | Priority date | Publication date | Assignee | Title |
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CN102059247A (en) * | 2010-11-29 | 2011-05-18 | 中国科学院地理科学与资源研究所 | Vehicle-mounted repairing equipment and method for polluted site soil and underground water body |
CN102500612A (en) * | 2011-10-28 | 2012-06-20 | 中南大学 | Chemical leaching restoring method for soil polluted by heavy metals |
CN102598911A (en) * | 2012-03-29 | 2012-07-25 | 常熟市佳盛农业科技发展有限公司 | Method for remedying heavy metal polluted mining soil |
CN102873086A (en) * | 2012-10-09 | 2013-01-16 | 北京大学 | Mercury contaminated soil in-situ restoration method |
CN102896140A (en) * | 2012-10-25 | 2013-01-30 | 北京中持绿色能源环境技术有限公司 | In-situ biological treating method for municipal solid waste landfill |
CN103981875A (en) * | 2013-12-05 | 2014-08-13 | 青岛理工大学 | Landfill method capable of synchronously stabilizing chromium slag and household garbage |
CN103981097A (en) * | 2013-12-05 | 2014-08-13 | 青岛理工大学 | Preparation method of remediation flora for Cr (VI) contaminated site from sludge |
CN103978025A (en) * | 2013-12-05 | 2014-08-13 | 青岛理工大学 | Landfill method for rapid stabilization of chromium-containing soil and household garbage |
CN104275347A (en) * | 2014-10-22 | 2015-01-14 | 天津生态城环保有限公司 | Medicament injection device for in-situ remediation of pollution site |
CN105414163A (en) * | 2015-11-09 | 2016-03-23 | 四川龙蟒钛业股份有限公司 | Method for repairing cadmium contaminated soil |
CN105344705A (en) * | 2015-11-27 | 2016-02-24 | 上海岩土工程勘察设计研究院有限公司 | Injection device for in-situ remediation of contaminated sites |
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Application publication date: 20161012 |