CN105665438B - A kind of method of the soil petroleum hydrocarbon contaminated using phytoremediation severe - Google Patents
A kind of method of the soil petroleum hydrocarbon contaminated using phytoremediation severe Download PDFInfo
- Publication number
- CN105665438B CN105665438B CN201610020535.4A CN201610020535A CN105665438B CN 105665438 B CN105665438 B CN 105665438B CN 201610020535 A CN201610020535 A CN 201610020535A CN 105665438 B CN105665438 B CN 105665438B
- Authority
- CN
- China
- Prior art keywords
- soil
- petroleum hydrocarbon
- selenium
- plant
- contaminated
- 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.)
- Active
Links
- 239000002689 soil Substances 0.000 title claims abstract description 134
- 239000003209 petroleum derivative Substances 0.000 title claims abstract description 53
- 238000000034 method Methods 0.000 title claims abstract description 14
- 239000011669 selenium Substances 0.000 claims abstract description 56
- 229910052711 selenium Inorganic materials 0.000 claims abstract description 55
- 229940091258 selenium supplement Drugs 0.000 claims abstract description 55
- BUGBHKTXTAQXES-UHFFFAOYSA-N Selenium Chemical compound [Se] BUGBHKTXTAQXES-UHFFFAOYSA-N 0.000 claims abstract description 54
- 239000011781 sodium selenite Substances 0.000 claims abstract description 37
- BVTBRVFYZUCAKH-UHFFFAOYSA-L disodium selenite Chemical compound [Na+].[Na+].[O-][Se]([O-])=O BVTBRVFYZUCAKH-UHFFFAOYSA-L 0.000 claims abstract description 36
- 235000015921 sodium selenite Nutrition 0.000 claims abstract description 36
- 229960001471 sodium selenite Drugs 0.000 claims abstract description 30
- 230000007613 environmental effect Effects 0.000 claims abstract description 13
- 238000012545 processing Methods 0.000 claims abstract description 9
- 229930195733 hydrocarbon Natural products 0.000 claims abstract description 7
- 150000002430 hydrocarbons Chemical class 0.000 claims abstract description 7
- 239000004215 Carbon black (E152) Substances 0.000 claims abstract description 6
- 241000196324 Embryophyta Species 0.000 claims description 26
- 241000219793 Trifolium Species 0.000 claims description 8
- 244000026873 Alternanthera philoxeroides Species 0.000 claims description 6
- 241000143476 Bidens Species 0.000 claims description 6
- 235000010662 Bidens pilosa Nutrition 0.000 claims description 6
- 239000010410 layer Substances 0.000 claims description 5
- 238000009331 sowing Methods 0.000 claims description 5
- 235000013311 vegetables Nutrition 0.000 claims description 4
- 238000011109 contamination Methods 0.000 claims description 3
- 239000004575 stone Substances 0.000 claims description 3
- 239000002344 surface layer Substances 0.000 claims description 3
- 239000002283 diesel fuel Substances 0.000 claims description 2
- 230000000694 effects Effects 0.000 abstract description 5
- 230000009286 beneficial effect Effects 0.000 abstract description 2
- 238000001514 detection method Methods 0.000 abstract description 2
- 238000002474 experimental method Methods 0.000 abstract description 2
- 230000000243 photosynthetic effect Effects 0.000 abstract description 2
- 229910003424 Na2SeO3 Inorganic materials 0.000 description 7
- 238000005507 spraying Methods 0.000 description 7
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 7
- 238000012360 testing method Methods 0.000 description 6
- 244000005700 microbiome Species 0.000 description 5
- 238000011161 development Methods 0.000 description 3
- 230000018109 developmental process Effects 0.000 description 3
- 239000003208 petroleum Substances 0.000 description 3
- FMMWHPNWAFZXNH-UHFFFAOYSA-N Benz[a]pyrene Chemical compound C1=C2C3=CC=CC=C3C=C(C=C3)C2=C2C3=CC=CC2=C1 FMMWHPNWAFZXNH-UHFFFAOYSA-N 0.000 description 2
- 240000008916 Oenothera biennis Species 0.000 description 2
- 235000004496 Oenothera biennis Nutrition 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 229940045761 evening primrose extract Drugs 0.000 description 2
- 235000008524 evening primrose extract Nutrition 0.000 description 2
- 238000005067 remediation Methods 0.000 description 2
- 239000004094 surface-active agent Substances 0.000 description 2
- TXVHTIQJNYSSKO-UHFFFAOYSA-N BeP Natural products C1=CC=C2C3=CC=CC=C3C3=CC=CC4=CC=C1C2=C34 TXVHTIQJNYSSKO-UHFFFAOYSA-N 0.000 description 1
- 244000025254 Cannabis sativa Species 0.000 description 1
- 241000238631 Hexapoda Species 0.000 description 1
- 241001465754 Metazoa Species 0.000 description 1
- 241000736262 Microbiota Species 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 201000010099 disease Diseases 0.000 description 1
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 230000035784 germination Effects 0.000 description 1
- 230000012010 growth Effects 0.000 description 1
- 238000011065 in-situ storage Methods 0.000 description 1
- 210000003734 kidney Anatomy 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 210000004185 liver Anatomy 0.000 description 1
- 230000008635 plant growth Effects 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 125000005575 polycyclic aromatic hydrocarbon group Chemical group 0.000 description 1
- 230000008929 regeneration Effects 0.000 description 1
- 238000011069 regeneration method Methods 0.000 description 1
- 125000003748 selenium group Chemical group *[Se]* 0.000 description 1
- SCWQRZHMKQEINE-UHFFFAOYSA-N selenous acid;sodium Chemical compound [Na].O[Se](O)=O SCWQRZHMKQEINE-UHFFFAOYSA-N 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 231100000419 toxicity Toxicity 0.000 description 1
- 230000001988 toxicity Effects 0.000 description 1
- 238000009966 trimming Methods 0.000 description 1
- 230000002792 vascular Effects 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
Classifications
-
- 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
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Mycology (AREA)
- Biotechnology (AREA)
- Health & Medical Sciences (AREA)
- Biomedical Technology (AREA)
- Botany (AREA)
- General Health & Medical Sciences (AREA)
- Microbiology (AREA)
- Molecular Biology (AREA)
- Soil Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
The present invention relates to a kind of method of the soil petroleum hydrocarbon contaminated using phytoremediation severe, the specific steps are：A certain amount of sodium selenite is added in high concentration petroleum hydrocarbon contaminated soil topsoil, topsoil selenium element content is made to reach selenium-rich level, plant seed is sowed or by seedling cultivation in the soil by selenium addition processing again, when plant grows to the maturity period, to plant-cutting or pull out, and harmless treatment is carried out, so repeatedly until soil oil hydrocarbon and PAHs content reaches environmental safety standard.Previous experiments are found, plant grows in high concentration petroleum hydrocarbon soil significantly to be inhibited, and after adding low dosage sodium selenite in the soil, detection finds that plant leaf blade photosynthetic capacity improves, root system decomposing petroleum hydrocarbon ability is remarkably reinforced, therefore the beneficial effects of the invention are as follows add low dosage selenium in soil to improve repairing effect of the plant to high concentration petroleum hydrocarbon.
Description
Technical field
The present invention relates to a kind of petroleum hydrocarbon contaminated plant restoration methods of the severe based on soil spraying selenium, are specially applied in soil
Add a certain amount of selenium, improve the plant tolerance and absorbability petroleum hydrocarbon contaminated to high concentration.
Background technology
Petroleum industry brings many environmental problems while rapid development.Oil exploration, exploitation, refinement, processing and
Often soil is polluted during transport, the processing of petroleum pollution has become countries in the world environment urgently to be resolved hurrily
One of problem.In these soil with serious petroleum pollution, pollutant load is high, is destroyed soil texture and function.According to
It investigates, the soil around the Oilfield Operation District of most of China generally all receives more serious oil pollution, some oil
Even not even a blade of grass grows for contaminated soil.Most component for several times in oil is particularly some unsaturation hydrocarbons, in soil
Animals and plants have very big toxic action, and wherein polycyclic aromatic hydrocarbon compounds (PAHs) toxicity is maximum, and crop germination and emergence rate is caused to drop
Low, setting percentage declines, and resistant to lodging, disease and insect resistance ability reduces, while structure of community and microbiota shadow to microorganism
Sound is larger so that the activity of contaminated soil further reduces.PAHs can also enter human body by food chain, influence liver, kidney and the heart
Vascular system generates harm to the mankind, even results in canceration.
Mainly there are three categories currently for the administering method of petroleum hydrocarbon contaminated soil：Physical, chemical method and biological prosthetic
Method.It is wherein biological prosthetic due to its processing cost is low, non-secondary pollution, can treatment in situ, public's acceptance level is high and effect is good
The advantages that, there is boundless development potentiality and application prospect.Biological prosthetic type mainly includes microorganism remediation, plant
Reparation and microorganism-plant combined reparation, wherein and microorganism-plant combined repair is that contaminated soil bioremediation technology is ground
The new development studied carefully, the advantages of having both microorganism remediation and phytoremediation.However, when soil petrochina hydrocarbon excessive concentration (is more than
20g/kg soil) when, not only Soil Microorganism is difficult to survive, and the growth of big portion plant can be also suppressed, existing biology
Restorative procedure is difficult to carry out.Currently the improvement of severe petroleum hydrocarbon contaminated soil is mainly handled using surfactant washing,
But the use of surfactant can bring secondary environmental pollution.Therefore, up to the present, high concentration petroleum hydrocarbon contaminated soil
Reparation is still a problem urgently to be resolved hurrily of environmental science.
Invention content
The technical problems to be solved by the invention are：A kind of administering method to high concentration petroleum hydrocarbon contaminated soil is provided,
By adding a certain amount of selenium to high concentration petroleum hydrocarbon contaminated soil, soil is made to reach selenium-rich level (1-2mg/kg soil), is carried
High plant is to the tolerance of high concentration petroleum hydrocarbon.
The technical solution adopted in the present invention is：A kind of high concentration petroleum hydrocarbon contaminated soil selenium fortification of plants restorative procedure.
The above method specifically includes following steps：
A certain amount of sodium selenite is added in the petroleum hydrocarbon contaminated upper soll layer of high concentration, contains topsoil selenium element
Amount reaches selenium-rich level, then serike seedling or sowing vegetable seeds on the soil by selenium addition processing, when plant is long
To the maturity period, plant is pulled out and carries out harmless treatment, so repeatedly until soil oil hydrocarbon content reaches Environmental security mark
It is accurate.Sodium selenite solution is specifically uniformly sprayed on to high concentration petroleum hydrocarbon contaminated soil surface, it is with tool that sodium selenite is molten
Liquid and the abundant mixing of surface layer 20cm depth soil.A certain amount of selenium is added to poor selenium soil, soil selenium contamination will not be caused, it can be with
Improve the physicochemical property of local soil.
Petroleum hydrocarbon contaminated soil includes oil pollution, contaminated by diesel oil, gasoline contamination or its mixed type contaminated soil.
A concentration of 20-50g/kg soil of petroleum hydrocarbon of the soil petrochina hydrocarbon pollution., under this concentration plant growth by
Apparent to inhibit, Soil Microorganism is difficult to survive.
The soil horizon surface layer refers to the soil horizon of soil depth 20cm, and the sodium selenite that addition is a little measured makes upper soll layer
Selenium-rich content reaches 1-2mg/kg.It is selenium-rich soil that Se content in soil usually is higher than 0.5mg/kg, and is poor selenium less than this value
Soil.In technical scheme of the present invention, it would be desirable to selenium amount be added to be scaled sodium selenite (Na2SeO3) quality, and by required selenous acid
Sodium is dissolved in water；
The plant seedlings or vegetable seeds include beggar-ticks, clover, Alternanthera philoxeroides.
Industrial sodium selenite is cheap, relatively low with present invention processing high concentration petroleum hydrocarbon contaminated soil control expense, real
Border application value is big.
A certain amount of sodium selenite is added in high concentration petroleum hydrocarbon contaminated soil topsoil, makes topsoil selenium element
Content reaches selenium-rich level, then plant seed is sowed or by seedling cultivation in the soil by selenium addition processing, works as plant
The maturity period is grown to, to plant-cutting or is pulled out, and carries out harmless treatment, so repeatedly until soil oil hydrocarbon and PAHs
Content reaches environmental safety standard.If benzo (a) pyrene content is less than 0.10mg/kg, that is, reach environmental safety standard.Energy of the present invention
Plant is improved to the petroleum hydrocarbon contaminated tolerance of soil middle and high concentration, and plant is promoted to absorb petroleum hydrocarbon, and repair time is short, carries
High effect of plant restoration.Since industrial sodium selenite is cheap, high concentration petroleum hydrocarbon contaminated soil expense is administered with the present invention
It is relatively low, there is higher actual application value.Previous experiments find that plant grows in high concentration petroleum hydrocarbon soil significantly to be pressed down
System, and after adding low dosage sodium selenite in the soil, detection finds that plant leaf blade photosynthetic capacity improves, root system degradation stone
Petroleum hydrocarbon ability is remarkably reinforced, therefore the beneficial effects of the invention are as follows add low dosage selenium in soil to improve plant to high concentration stone
The repairing effect of petroleum hydrocarbon.
Specific embodiment
Embodiment one
Area is 100m2Petroleum hydrocarbon serious pollution area, a concentration of 30g/kg soil of soil petroleum hydrocarbon after testing, Selenium in Soil
A concentration of 0.1mg/kg, soil density 25kg/m3.Topsoil selenium concentration is made to reach 1mg/kg, then soil should increase selenium
0.9mg/kg soil, sodium selenite (Na2SeO3) selenium element content for 46%, therefore dosage of sodium selenite is
1.9mg/kg is calculated：Area 100m2, depth 20cm soil need sodium selenite 0.98g, 0.98g sodium selenites are dissolved in 5L water,
And abundant mixing.Solution with spraying device is uniformly sprayed on to severe petroleum hydrocarbon contaminated soil surface, sprinkling area's soil is ploughed
0.2m is deep, makes mixing.By beggar-ticks seed be seeded in more than by plus selenium soil on, thickness of sowing is：100-200/m2,
When beggar-ticks grows to seed stage, which dial and is removed, and carry out harmless treatment, so repeatedly to soil greasy dirt content
Reach environmental safety standard.
Embodiment two
Area is 100m2Petroleum hydrocarbon serious pollution area, a concentration of 30g/kg soil of soil petroleum hydrocarbon after testing, Selenium in Soil
A concentration of 0.1mg/kg, soil density 25kg/m3.Topsoil selenium concentration is made to reach 1mg/kg, then soil should increase selenium
0.9mg/kg soil, sodium selenite (Na2SeO3) selenium element content for 46%, therefore dosage of sodium selenite is
1.9mg/kg is calculated：Area 100m2, depth 20cm soil need sodium selenite 0.98g, 0.98g sodium selenites are dissolved in 5L water,
And abundant mixing.Solution with spraying device is uniformly sprayed on to severe petroleum hydrocarbon contaminated soil surface, sprinkling area's soil is ploughed
0.2m is deep, makes mixing.By height about 5cm beggar-ticks seedling cultivation on the above soil by adding selenium, planting density is：
50-60 plants/m2, when beggar-ticks grows to seed stage, which dial and is removed, and carry out harmless treatment, so repeatedly extremely
Soil greasy dirt content reaches environmental safety standard.
Embodiment three
Area is 200m2Petroleum hydrocarbon serious pollution area, a concentration of 50g/kg soil of soil petroleum hydrocarbon after testing, Selenium in Soil
A concentration of 0.2mg/kg, soil density 25kg/m3.Topsoil selenium concentration is made to reach 2mg/kg, then soil should increase selenium
1.8mg/kg soil, sodium selenite (Na2SeO3) selenium element content be 46%.Therefore dosage of sodium selenite is
1.9mg/kg is calculated：Area 100m2, depth 20cm soil need sodium selenite 3.91g, 3.91g sodium selenites are dissolved in 10L water,
And abundant mixing.Solution with spraying device is uniformly sprayed on to severe petroleum hydrocarbon contaminated soil surface, sprinkling area's soil is ploughed
0.2m is deep, makes mixing.By clover seed be seeded in more than by plus selenium soil on, thickness of sowing is：200-400/m2,
When clover grows to 30cm high or so, plant top being cradled and harmless public processing, clover is herbaceos perennial,
Root tillering ability and power of regeneration are strong, resistance to trimming, and update leaflet can be grown in 10 days after cradling.So repeatedly to soil greasy dirt
Content reaches environmental safety standard.
Example IV
Area is 100m2Petroleum hydrocarbon serious pollution area, a concentration of 30g/kg soil of soil petroleum hydrocarbon after testing, Selenium in Soil
A concentration of 0.1mg/kg, soil density 25kg/m3.Topsoil selenium concentration is made to reach 1mg/kg, then soil should increase selenium
0.9mg/kg soil, sodium selenite (Na2SeO3) selenium element content for 46%, therefore dosage of sodium selenite is
1.9mg/kg is calculated：Area 100m2, depth 20cm soil need sodium selenite 0.98g, 0.98g sodium selenites are dissolved in 5L water,
And abundant mixing.Solution with spraying device is uniformly sprayed on to severe petroleum hydrocarbon contaminated soil surface, sprinkling area's soil is ploughed
0.2m is deep, makes mixing.By height about 10cm clover seedling kinds on the above soil by adding selenium, planting density is：
100-200 plants/m2, when clover grows to seed stage, which dial and is removed, and carry out harmless treatment, clover life
Life power is strong, and annual spring and autumn can respectively plant once, so reach environmental safety standard to soil greasy dirt content repeatedly.
Embodiment five
Area is 200m2Petroleum hydrocarbon serious pollution area, a concentration of 50g/kg soil of soil petroleum hydrocarbon after testing, Selenium in Soil
A concentration of 0.2mg/kg, soil density 25kg/m3.Topsoil selenium concentration is made to reach 2mg/kg, then soil should increase selenium
1.8mg/kg soil, sodium selenite (Na2SeO3) selenium element content be 46%.Therefore dosage of sodium selenite is
1.9mg/kg is calculated：Area 100m2, depth 20cm soil need sodium selenite 3.91g, 3.91g sodium selenites are dissolved in 10L water,
And abundant mixing.Solution with spraying device is uniformly sprayed on to severe petroleum hydrocarbon contaminated soil surface, sprinkling area's soil is ploughed
0.2m is deep, makes mixing.By Alternanthera philoxeroides seed be seeded in more than by plus selenium soil on, thickness of sowing is：200-300
Grain/m2, when Alternanthera philoxeroides grows to seed stage, oenothera biennis dial and is removed, and carry out harmless treatment, so repeatedly to soil
Greasy dirt content reaches environmental safety standard.
Embodiment six
Area is 100m2Petroleum hydrocarbon serious pollution area, a concentration of 30g/kg soil of soil petroleum hydrocarbon after testing, Selenium in Soil
A concentration of 0.1mg/kg, soil density 25kg/m3.Topsoil selenium concentration is made to reach 1mg/kg, then soil should increase selenium
0.9mg/kg soil, sodium selenite (Na2SeO3) selenium element content for 46%, therefore dosage of sodium selenite is
1.9mg/kg is calculated：Area 100m2, depth 20cm soil need sodium selenite 0.98g, 0.98g sodium selenites are dissolved in 5L water,
And abundant mixing.Solution with spraying device is uniformly sprayed on to severe petroleum hydrocarbon contaminated soil surface, sprinkling area's soil is ploughed
0.2m is deep, makes mixing.By height about 5cm Alternanthera philoxeroides seedling kinds on the above soil by adding selenium, planting density is：
50-60 plants/m2, when Alternanthera philoxeroides grows to seed stage, oenothera biennis dial and is removed, and carry out harmless treatment, so repeatedly
Reach environmental safety standard to soil greasy dirt content.
Claims (3)
- A kind of 1. method of the soil petroleum hydrocarbon contaminated using phytoremediation severe, which is characterized in that in the dirt of high concentration petroleum hydrocarbon A certain amount of sodium selenite is added in the upper soll layer of dye, making upper soll layer selenium-rich content, soil horizon surface layer is up to 1-2mg/kg Refer to the soil horizon of soil depth 20cm, a concentration of 20-50g/kg soil of petroleum hydrocarbon of the petroleum hydrocarbon contaminated upper soll layer of the high concentration Earth, then serike seedling or sowing vegetable seeds on the soil by selenium addition processing, when plant grows to the maturity period, will plant Object is pulled out and carries out harmless treatment, so repeatedly until soil oil hydrocarbon content reaches environmental safety standard.
- 2. the method for the soil petroleum hydrocarbon contaminated using phytoremediation severe according to claim 1, which is characterized in that stone Petroleum hydrocarbon contaminated soil includes oil pollution, contaminated by diesel oil, gasoline contamination or its mixed type contaminated soil.
- 3. the method for the soil petroleum hydrocarbon contaminated using phytoremediation severe according to claim 1, which is characterized in that institute The plant seedlings or vegetable seeds stated include beggar-ticks, clover, Alternanthera philoxeroides.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201610020535.4A CN105665438B (en) | 2016-01-13 | 2016-01-13 | A kind of method of the soil petroleum hydrocarbon contaminated using phytoremediation severe |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201610020535.4A CN105665438B (en) | 2016-01-13 | 2016-01-13 | A kind of method of the soil petroleum hydrocarbon contaminated using phytoremediation severe |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN105665438A CN105665438A (en) | 2016-06-15 |
| CN105665438B true CN105665438B (en) | 2018-06-19 |
Family
ID=56300258
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201610020535.4A Active CN105665438B (en) | 2016-01-13 | 2016-01-13 | A kind of method of the soil petroleum hydrocarbon contaminated using phytoremediation severe |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN105665438B (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN109465284A (en) * | 2018-12-04 | 2019-03-15 | 三峡大学 | A kind of method that organosilicon addition enhancing plant soil restoration severe is petroleum hydrocarbon contaminated |
Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1792483A (en) * | 2006-01-06 | 2006-06-28 | 中国科学院南京土壤研究所 | Process of botany for repairing soil composite polluted by polycyclic aromatic hydrocarbon |
| CN101433905A (en) * | 2008-12-25 | 2009-05-20 | 南开大学 | Method for repairing oil polluted soil using ornamental plant balsamine |
| CN102601102A (en) * | 2012-02-09 | 2012-07-25 | 中国科学院生态环境研究中心 | Method for repairing high-concentration oil-polluted soil through mycorrhizal fungi-plant-degradation bacterium |
| CN102744247A (en) * | 2011-11-09 | 2012-10-24 | 长安大学 | Method for restoring petroleum-contaminated soil by using Trifolium repens Linn |
| CN104117533A (en) * | 2013-04-25 | 2014-10-29 | 成都新朝阳作物科学有限公司 | Combined application of selenium-containing agricultural preparation and soil heavy metal remediation agent |
-
2016
- 2016-01-13 CN CN201610020535.4A patent/CN105665438B/en active Active
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1792483A (en) * | 2006-01-06 | 2006-06-28 | 中国科学院南京土壤研究所 | Process of botany for repairing soil composite polluted by polycyclic aromatic hydrocarbon |
| CN101433905A (en) * | 2008-12-25 | 2009-05-20 | 南开大学 | Method for repairing oil polluted soil using ornamental plant balsamine |
| CN102744247A (en) * | 2011-11-09 | 2012-10-24 | 长安大学 | Method for restoring petroleum-contaminated soil by using Trifolium repens Linn |
| CN102601102A (en) * | 2012-02-09 | 2012-07-25 | 中国科学院生态环境研究中心 | Method for repairing high-concentration oil-polluted soil through mycorrhizal fungi-plant-degradation bacterium |
| CN104117533A (en) * | 2013-04-25 | 2014-10-29 | 成都新朝阳作物科学有限公司 | Combined application of selenium-containing agricultural preparation and soil heavy metal remediation agent |
Non-Patent Citations (3)
| Title |
|---|
| 我国石油污染土壤修复研究现状与展望;邓绍云 等;《北方园艺》;20121231(第14期);第184-190页 * |
| 硒增强植物抗逆能力及其机理研究进展;贾玮 等;《中国农学通报》;20151231;第31卷(第14期);第171-176页 * |
| 硒提高植物拮抗重金属毒性的研究进展;吴之琳 等;《粮食科技与经济》;20140424;第39卷(第2期);第22页第1节 * |
Also Published As
| Publication number | Publication date |
|---|---|
| CN105665438A (en) | 2016-06-15 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN104529668B (en) | Metal mine soil conditioner, and mine ecological remediation method using metal mine soil conditioner. | |
| CN104550208B (en) | A kind of farmland soil heavy metals pollution amelioration method of coupling activation and passivation | |
| CN100518970C (en) | Renovation method for plant in soil of zinc-cadmium combined pollution | |
| CN107138511B (en) | Method for combined remediation of heavy metal contaminated soil | |
| CN101758068B (en) | Method for continuously repairing heavy metal in soil by using chelating agent | |
| CN101116865A (en) | Method for producing and restoring vegetables growing in the heavy metal mildly-polluted soil | |
| CN101704015A (en) | Method for improving phytoremediation efficiency of low-concentration arsenic-contaminated soil | |
| CN109746255A (en) | A kind of method of activator joint Phytoremediation of Soils Contaminated by Heavy Metals | |
| CN102172608A (en) | Application of artemisia stolonifera in repairing of heavy metal cadmium polluted soil | |
| CN103586270A (en) | Method for restoring heavy metal contaminated soil | |
| CN107159694A (en) | A kind of heavy metal pollution of soil restorative procedure | |
| CN104871850A (en) | Method for improving repairing efficiency of heavy metal polluted plants | |
| CN103858554A (en) | Method for governing and improving soda saline and alkaline land through magnet tailing composite modifying agents | |
| CN105772501B (en) | A kind of plant restoration method of underground pollution | |
| CN109622601B (en) | Method for restoring farmland soil polluted by low-concentration mercury by utilizing cotton and Indian mustard crop rotation | |
| CN109158414A (en) | A kind of plant extract in heavy metal pollution farmland-chemical passivation combined remediation method | |
| CN1981947A (en) | Method for repairing soil polluted by arsenic by plant | |
| CN104289508A (en) | Biological remediation method for soil polluted by heavy metals | |
| CN108246798A (en) | Utilize the method for spray seeding technique restoration of soil polluted by heavy metal | |
| CN102189096A (en) | Remediation method for lead contamination in mine soil | |
| Dagar | Opportunities for alternate land uses in salty and water scarcity areas | |
| CN105665438B (en) | A kind of method of the soil petroleum hydrocarbon contaminated using phytoremediation severe | |
| CN103406348A (en) | Application of Youngia erythrocarpa in restoration of orchard soil contaminated by heavy metal cadmium | |
| CN105330485A (en) | Leaf fertilizer for preventing crops from absorbing cadmium and application thereof | |
| CN108097711A (en) | A kind of method for repairing Grown In Zinc Contaminated Soil using penicillium janthinellum joint Indian mustard |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| C10 | Entry into substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| CB03 | Change of inventor or designer information |
Inventor after: Huang Yingping Inventor after: Song Yizhi Inventor after: Liu Huigang Inventor after: Huang Jueying Inventor before: Huang Yingping Inventor before: Liu Huigang Inventor before: Song Yizhi Inventor before: Huang Jueying |
|
| CB03 | Change of inventor or designer information | ||
| GR01 | Patent grant | ||
| GR01 | Patent grant | ||
| OL01 | Intention to license declared |