CN109772877A - Chemical pollution site remediation method - Google Patents
Chemical pollution site remediation method Download PDFInfo
- Publication number
- CN109772877A CN109772877A CN201811651983.XA CN201811651983A CN109772877A CN 109772877 A CN109772877 A CN 109772877A CN 201811651983 A CN201811651983 A CN 201811651983A CN 109772877 A CN109772877 A CN 109772877A
- Authority
- CN
- China
- Prior art keywords
- parts
- chemical pollution
- microorganism
- soil
- remediation method
- 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
Links
Abstract
The present invention provides a kind of chemical pollution site remediation method.It is of the invention that this method comprises the following steps: (1) to chemical pollution place carry out it is smooth after be isolated;(2) microorganism remediation is used, repairing efficiency is 6-12 months;(3) it ploughs to the soil after microorganism remediation, it is smooth;(4) vegetation repair is used, repairing efficiency is 12-24 months;(5) vegetation is removed, the content of pollutant in soil after repairing is detected, step (2) are repeated if exceeded and arrive step (4), until contaminated ground detection is up to standard.Repairing effect of the present invention is good, at low cost.
Description
Technical field:
The present invention relates to a kind of chemical pollution site remediation methods, belong to environmental engineering technical field.
Background technique:
Pollution on the environment is mainly the pollution of organic matter and inorganic wastes, these substances can be long by osmosis
Phase infiltrates soil, causes adsorption by soil noxious material.The poisonous substance in chemical plant is extremely complex, different types of chemical plant feature pollution
Object is different, the waste of some discharge sulfur-bearings containing ammonia, also has containing benzene, aldehyde, ether material, chemical characteristic is different, the extent of injury
It is different.Some plot are seriously polluted, used in the case where no progress soil remediation by exploitation, give body health of people
Bring grave danger.
Currently used restorative procedure has a transposition repairing and in-situ immobilization, main mode have soil replacement and backfilling, dilution of pouring water,
In drying and processing backfill and lime and waiting, the reparation difficulty of these methods is big, the period is long, at high cost, one hectare of contaminated land,
Rehabilitation expense several hundred million members or more than ten00000000 yuan easily, of such a size capital investment, enterprise is difficult to bear.
Summary of the invention:
The purpose of the present invention is providing a kind of chemical pollution site remediation method in view of the above problems, repairing effect is good,
It is at low cost.
Above-mentioned purpose is realized by following technical scheme:
A kind of chemical pollution site remediation method, this method comprises the following steps:
(1) to chemical pollution place carry out it is smooth after be isolated;
(2) microorganism remediation is used, repairing efficiency is 6-12 months;
(3) it ploughs to the soil after microorganism remediation, it is smooth;
(4) vegetation repair is used, repairing efficiency is 12-24 months;
(5) vegetation is removed, the content of pollutant in soil after repairing is detected, step (2) are repeated if exceeded and arrive step (4),
Until contaminated ground detection is up to standard.
The chemical pollution site remediation method, it is as described in step (1) smooth laggard to the progress of chemical pollution place
The specific method of row isolation is: carrying out block divider wall to contaminated place first, the height of divider wall is not less than contaminated place
Contaminated place highest point;It builds divider wall and carries out prepartion of land later.
The chemical pollution site remediation method, microorganism remediation described in step (2) specifically make first
Microorganism renovation agent, the microorganism renovation agent include moving 5-12 parts of glue bacterium, 3-6 parts of cyanobacteria, sulfate also in parts by weight
5-13 parts of opportunistic pathogen, 2-6 parts of citric acid bacterium, 5-9 parts of pseudomonas syringae, 3-8 parts of Escherichia coli, bacillus subtilis 10-15
Part, 7-14 parts of staphylococcus, 1-3 parts of black-koji mould, 6-9 parts of bafillus natto, 5-10 parts of Thiobacillus, make microorganism and repair
After multiple agent, by the microorganism renovation agent made and broad-spectrum culture according to the ratio of mass ratio 1:1, uniformly launch to be repaired
Soil on, then sprinkle water.
The chemical pollution site remediation method, the broad-spectrum culture use brewer's wort.
The chemical pollution site remediation method, the amount of the watering are 2-3.5 kg of water/square metre soils, are spilt
The gap periods of water are 7-15 days.
The chemical pollution site remediation method, step is ploughed described in (3), including is ploughed at least twice, is ploughed
Depth is not less than 50cm.
The chemical pollution site remediation method, the vegetation repair refer to plantation willow, sunflower, India's grass,
The spacing in the rows of the willow is 150-180cm, plants sunflower in the interval of plantation willow, and the spacing in the rows of sunflower is 50-65cm,
Then intensively plantation India is careless again.
The utility model has the advantages that
The method that the present invention uses microorganism remediation and vegetation repair to combine, first using microorganism remediation to a huge sum of money in soil
Category is fixed, moves or converts, and changes their environmental chemical behavio4s in the soil, can promote poisonous and harmful substances removing toxic substances
Or toxicity is reduced, and to achieve the purpose that biological prosthetic, belong to based technique for in-situ remediation, it is at low cost, secondary pollution is easily controllable,
After microorganism remediation, then using vegetation repair recovery soil environment, repairing effect is good, at low cost.
Specific embodiment:
A kind of chemical pollution site remediation method of the invention, this method comprises the following steps:
(1) to chemical pollution place carry out it is smooth after be isolated;
(2) microorganism remediation is used, repairing efficiency is 6-12 months;
(3) it ploughs to the soil after microorganism remediation, it is smooth;
(4) vegetation repair is used, repairing efficiency is 12-24 months;
(5) vegetation is removed, the content of pollutant in soil after repairing is detected, step (2) are repeated if exceeded and arrive step (4),
Until contaminated ground detection is up to standard.
The chemical pollution site remediation method, it is as described in step (1) smooth laggard to the progress of chemical pollution place
The specific method of row isolation is: carrying out block divider wall to contaminated place first, the height of divider wall is not less than contaminated place
Contaminated place highest point;It builds divider wall and carries out prepartion of land later.
The chemical pollution site remediation method, microorganism remediation described in step (2) specifically make first
Microorganism renovation agent, the microorganism renovation agent include moving 5-12 parts of glue bacterium, 3-6 parts of cyanobacteria, sulfate also in parts by weight
5-13 parts of opportunistic pathogen, 2-6 parts of citric acid bacterium, 5-9 parts of pseudomonas syringae, 3-8 parts of Escherichia coli, bacillus subtilis 10-15
Part, 7-14 parts of staphylococcus, 1-3 parts of black-koji mould, 6-9 parts of bafillus natto, 5-10 parts of Thiobacillus, make microorganism and repair
After multiple agent, by the microorganism renovation agent made and broad-spectrum culture according to the ratio of mass ratio 1:1, uniformly launch to be repaired
Soil on, broad-spectrum culture use brewer's wort.Then it sprinkles water.The amount of watering is 2-3.5 kg of water/square metre soil,
The gap periods of watering are 7-15 days.
The chemical pollution site remediation method, step is ploughed described in (3), including is ploughed at least twice, is ploughed
Depth is not less than 50cm.It ploughs one month to two months preferably spaced apart and carries out twice, deeper bred convenient for microorganism, repair effect
Fruit is more preferably.
The chemical pollution site remediation method, the vegetation repair refer to plantation willow, sunflower, India's grass,
The spacing in the rows of the willow is 150-180cm, plants sunflower in the interval of plantation willow, and the spacing in the rows of sunflower is 50-65cm,
Then intensively plantation India is careless again.
The above is only highly preferred embodiment of the present invention, the method for the present invention includes but be not limited to the above embodiments, the present invention
Unaccomplished matter, belong to the common knowledge of those skilled in the art.
Claims (7)
1. a kind of chemical pollution site remediation method, it is characterized in that: this method comprises the following steps:
(1) to chemical pollution place carry out it is smooth after be isolated;
(2) microorganism remediation is used, repairing efficiency is 6-12 months;
(3) it ploughs to the soil after microorganism remediation, it is smooth;
(4) vegetation repair is used, repairing efficiency is 12-24 months;
(5) vegetation is removed, the content of pollutant in soil after repairing is detected, step (2) are repeated if exceeded and arrive step (4),
Until contaminated ground detection is up to standard.
2. chemical pollution site remediation method according to claim 1, it is characterized in that: as described in step (1) to chemical industry
Contaminated site carry out it is smooth after the specific method be isolated be: block divider wall is carried out to contaminated place first, divider wall
Height is contaminated place highest point not less than contaminated place;It builds divider wall and carries out prepartion of land later.
3. chemical pollution site remediation method according to claim 1, it is characterized in that: microorganism described in step (2)
Repair, specifically, production microorganism renovation agent first, the microorganism renovation agent include in parts by weight dynamic 5-12 parts of glue bacterium,
3-6 parts of cyanobacteria, 5-13 parts of sulfate reducing bacteria, 2-6 parts of citric acid bacterium, 5-9 parts of pseudomonas syringae, Escherichia coli 3-8
Part, 10-15 parts of bacillus subtilis, 7-14 parts of staphylococcus, 1-3 parts of black-koji mould, 6-9 parts of bafillus natto, Thiobacillus
5-10 parts, after making microorganism renovation agent, by the microorganism renovation agent made and broad-spectrum culture according to mass ratio 1:1's
Ratio is uniformly launched onto soil to be repaired, is then sprinkled water.
4. chemical pollution site remediation method according to claim 3, it is characterized in that: the broad-spectrum culture uses wheat
Bud juice.
5. chemical pollution site remediation method according to claim 3, it is characterized in that: the amount of the watering is 2-3.5
Kg of water/square metre soil, the gap periods of watering are 7-15 days.
6. chemical pollution site remediation method according to claim 1 is wrapped it is characterized in that: ploughing described in step (3)
It includes and ploughs at least twice, depth of ploughing is not less than 50cm.
7. chemical pollution site remediation method according to claim 1, it is characterized in that: the vegetation repair refers to plantation
Willow, sunflower, India's grass, the spacing in the rows of the willow are 150-180cm, plant sunflower in the interval of plantation willow, to
Day, the spacing in the rows of certain herbaceous plants with big flowers was 50-65cm, and then intensively plantation India is careless again.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201811651983.XA CN109772877A (en) | 2018-12-31 | 2018-12-31 | Chemical pollution site remediation method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201811651983.XA CN109772877A (en) | 2018-12-31 | 2018-12-31 | Chemical pollution site remediation method |
Publications (1)
Publication Number | Publication Date |
---|---|
CN109772877A true CN109772877A (en) | 2019-05-21 |
Family
ID=66499052
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201811651983.XA Pending CN109772877A (en) | 2018-12-31 | 2018-12-31 | Chemical pollution site remediation method |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN109772877A (en) |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105170621A (en) * | 2015-09-30 | 2015-12-23 | 河南行知专利服务有限公司 | Method for restoring heavy metal contaminated soil through activating agent and microorganism reinforced plants |
CN105170642A (en) * | 2015-09-30 | 2015-12-23 | 河南行知专利服务有限公司 | Restoration method for industrial waste land soil heavy metal contamination |
CN106001103A (en) * | 2016-06-29 | 2016-10-12 | 惠州市东江园林工程有限公司 | Ecological restoration method for soil in chemical industrial area |
CN107488620A (en) * | 2017-10-08 | 2017-12-19 | 中国科学院成都生物研究所 | A kind of cadmium pollution paddy soil microorganism passivator |
-
2018
- 2018-12-31 CN CN201811651983.XA patent/CN109772877A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105170621A (en) * | 2015-09-30 | 2015-12-23 | 河南行知专利服务有限公司 | Method for restoring heavy metal contaminated soil through activating agent and microorganism reinforced plants |
CN105170642A (en) * | 2015-09-30 | 2015-12-23 | 河南行知专利服务有限公司 | Restoration method for industrial waste land soil heavy metal contamination |
CN106001103A (en) * | 2016-06-29 | 2016-10-12 | 惠州市东江园林工程有限公司 | Ecological restoration method for soil in chemical industrial area |
CN107488620A (en) * | 2017-10-08 | 2017-12-19 | 中国科学院成都生物研究所 | A kind of cadmium pollution paddy soil microorganism passivator |
Non-Patent Citations (6)
Title |
---|
孙英杰等: "《冶金企业污染土壤和地下水整治与修复》", 31 January 2008, 冶金工业出版社 * |
廖润华等: "《环境治理功能材料》", 30 April 2017, 中国建材工业出版社 * |
张进良等: "解磷微生物在农业应用中的研究进展 ", 《商丘师范学院学报》 * |
杨卓等: "《重金属污染土壤的植物修复及其强化技术研究》", 31 July 2014, 吉林人民出版社 * |
胡凯光等: "《微生物技术及应用》", 28 February 2015, 北京理工大学出版社 * |
郭书海等: "《污染土壤电动修复原理与技术》", 31 December 2017, 中国环境出版社 * |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN106001097B (en) | A method of joint repairs DDTs-PAHs combined contamination soil | |
US20170196227A1 (en) | Biological product for clearing of water, industrial wastewater and soil from chemicals, which are resistant to degradation and method for using the same | |
CN103480644A (en) | Plant-microorganism combined method for enhanced repairing of petroleum-contaminated spetroleum | |
CN104907330B (en) | A kind of biology in situ renovation method of nitro compound contaminated soil | |
CN101433905B (en) | Method for repairing oil polluted soil using ornamental plant balsamine | |
KR101705578B1 (en) | Composition for ecological restoration using and method for restoring the degraded ecology by them | |
CN106613588A (en) | Method for cyclically repairing cadmium-contaminated rice field and planting rice | |
CN104226679B (en) | A kind of method using antimicrobial plant combine d bioremediation manufactured coal gas plant contaminated soil | |
Sunday et al. | Management of petroleum impacted soil with phytoremediation and soil amendments in Ekpan Delta State, Nigeria | |
CN108655162B (en) | Method for restoring soil heavily polluted by petroleum | |
WO2004089831A3 (en) | Stable self-organizing plant-organism systems for remediating polluted soils and waters | |
CN110624949B (en) | Method for repairing excessive phosphorus pollution of phosphorite waste land by combining indigenous microorganisms and plants | |
RU2515691C1 (en) | Method of bioremediation of cadmium-contaminated soils | |
CN106583430A (en) | Method for repairing arsenium-polluted farmland soil through microorganisms and plants in combined manner | |
CN106734184A (en) | A kind of in-situ remediation method of heavy-metal contaminated soil | |
CN108188162A (en) | A kind of serious pollution land method | |
CN105195504A (en) | Method for restoring cadmium-terramycin combinedly contaminated soil through combination of plant and degrading bacterium | |
CN103146608B (en) | AMF+PGPR (arbuscular mycorrhizal fungi+plant growth promoting rhizobacteria) combined microbial inoculum and preparation method and application of combined microbial inoculum in decomposition of residual organophosphorus pesticides decomposition | |
CN109092882B (en) | In-situ ecological restoration method for composite contaminated soil by using biological and carbonized materials | |
CN109127693B (en) | Method for restoring Cu, Pb and As polluted soil by inoculating sunflower and castor with bacillus subtilis | |
RU2569582C1 (en) | Method of reclamation of tailing dump surface, which comprises toxic wastes, using phototrophic bacteria | |
RU2421291C2 (en) | Method to reclaim soils contaminated with oil and oil products | |
CN107552550A (en) | A kind of method that cadmium, lead-contaminated soil are repaired using root exudates fortification of plants | |
CN108246785A (en) | A kind of method for enhancing phytoremediation polycyclic aromatic hydrocarbon pollution efficiency | |
CN109772877A (en) | Chemical pollution site remediation method |
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 | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20190521 |