CN101091957B - Method for restoring petroleum polluted soil by microbe - Google Patents

Method for restoring petroleum polluted soil by microbe Download PDF

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Publication number
CN101091957B
CN101091957B CN2007100558978A CN200710055897A CN101091957B CN 101091957 B CN101091957 B CN 101091957B CN 2007100558978 A CN2007100558978 A CN 2007100558978A CN 200710055897 A CN200710055897 A CN 200710055897A CN 101091957 B CN101091957 B CN 101091957B
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soil
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days
moisture content
content
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CN101091957A (en
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冯江
王小雨
王升忠
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Northeast Normal University
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Northeast Normal University
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Abstract

The invention relates to a method to restore soil polluted by petroleum by adopting microorganism and the surface active agent produced by the microorganism. The invention restores the soil by adopting two strains of high efficiency degradation fungus Rhodococcus erythropolis and Pseudomonas aeruginosa and the surface active agent from Rhodococcus erythropolis. It can sharply improve degradation efficiency of soil petroleum hydrocarbon. The sample soil contains petroleum hydrocarbon 6500-8500 mg/kg, after degradation 25-60 days' degradation, the total petroleum hydrocarbon content is 1600-600mg/kg, and degradation efficiency is 80-93%.

Description

The repairing method of microorganism of oil-polluted soils
Technical field
The invention belongs to restorative procedure, be specifically related to utilize the biosurfactant reparation of microorganism and generation thereof to be subjected to the method for petroleum hydrocarbon contaminated soil northern wetland oilfield exploitation district to contaminated soil.
Background technology
Along with developing rapidly of China Petroleum, set up the oil field of different scales in many wetland zones, petroleum-polluted wetland area is also more and more.For example, Daqing oil field and Jilin Oil Field are positioned at the wetland district of two sides, downstream, Nenjiang, song-Nen plain innerland, and the Liaohe Oil Field is positioned at Liaohe delta wetland district, and Jilin Oil Field part mining area has entered south, Mo Moge nature reserve area and looked into the nature reserve area, dry lake.The foundation in oil field is very remarkable to the infringement of wetlands ecosystems, the deterioration that pollution sources such as the discarded slurry that oil exploration and a plurality of links such as drilling well, underground work and oil recovery in the development process are produced, ground crude oil, greasy filth and transportation and storage process all can bring well site and near soil soil property thereof has destroyed the ecological environment of wetlands ecosystems.Soil pollution petroleum hydrocarbon problem shows especially day by day, and Wetland ecological environment and biology are constituted a serious threat.
The common method of the petroleum hydrocarbon contaminated reparation of soil comprises: physics, chemistry and biological method.Compare with chemical method with physics, biological restoration particularly microorganism is repaired and to be had characteristics such as cost is low, environmental friendliness, is one of developing direction of the tool potentiality of the petroleum hydrocarbon contaminated reparation of soil.
Exist the microorganism of a large amount of dependence organic matter lives in the soil,, have the organic huge ability of oxidation Decomposition as bacterium, fungi, actinomyces etc.After being subjected to oil pollution, some microorganisms produce the enzyme system of decomposing pollutant under the inducing of pollutant, contaminant degradation can be transformed.
Summary of the invention
The synergy reparation that the present invention utilizes the wetland oilfield exploitation to distinguish from the biosurfactant (sugar esters compounds) of 2 high-efficiency degradation bacterium-rhodococcus erythropolis (Rhodococcus erythropolis) that screening obtains and verdigris first monad (Pseudomonas aeruginosa) and rhodococcus erythropolis (more than be known bacterial classification) generation is subjected to petroleum hydrocarbon contaminated soil, and the present invention can improve the degradation efficiency of soil petroleum hydrocarbon significantly.
The present invention is achieved by following technical proposals:
(1) will gather greasy dirt soil near the oil well, air-dry 20 ~ 30 days, remove volatile hydrocarbon and moisture content.
(2) rhodococcus erythropolis and verdigris first monad are cooperated Mixed Microbes in 1: 1 ratio, it is in 6500 ~ 8500mg/kg soil that bacterium liquid is inserted the total petroleum hydrocarbon initial content, and connecing the bacterium amount is 1.0 * 10 8~ 1.5 * 10 8Individual/g soil, add 1000 ~ 2000mg/kg biosurfactant again, add nutritive salt (nitrogenous source and phosphorus source), add H simultaneously 2O 25 ~ 10mg.
(3) add 5 ~ 10% wood chips and mix, and the adjusting moisture content is 15 ~ 25%.With the vessel surface covered with plastic film, prick the hole ventilation, degraded 50 ~ 60 days down at 25 ~ 30 ℃.
Implementation result
Tried that the total petroleum hydrocarbon initial content is 6500 ~ 8500mg/kg in the soil, after 25 ~ 60 days degraded, total petroleum hydrocarbons content is 1600 ~ 600mg/kg in the soil, and degradation efficiency is 80 ~ 93%.
The specific embodiment
Embodiment 1
(1) will gather greasy dirt soil near the oil well, air-dry 30 days, remove volatile hydrocarbon and moisture content.
(2) rhodococcus erythropolis and verdigris first monad are cooperated Mixed Microbes in 1: 1 ratio, it is in the 8037mg/kg soil that bacterium liquid is inserted the total petroleum hydrocarbon initial content, and connecing the bacterium amount is 1.1 * 10 8Individual/g soil, add the 1000mg/kg biosurfactant again, add KNO 3And K 2HPO 4As nutritive salt, add H simultaneously 2O5mg.
(3) add 6% wood chip and mix, and the adjusting moisture content is 25%.With the vessel surface covered with plastic film, prick the hole ventilation, total petroleum hydrocarbons content is 597mg/kg in the soil after 30 ℃ were degraded 58 days down, degradation efficiency is 93%.
Embodiment 2
(1) will gather greasy dirt soil near the oil well, air-dry 25 days, remove volatile hydrocarbon and moisture content.
(2) rhodococcus erythropolis liquid and verdigris first monad cooperate Mixed Microbes in 1: 1 ratio, and inserting the total petroleum hydrocarbon initial content is in the 8460mg/kg soil, and connecing the bacterium amount is 1.5 * 10 8Individual/g soil, add the 2000mg/kg biosurfactant, add KNO 3And K 2HPO 4As nutritive salt, add H simultaneously 2O 27mg.
(3) add 8% wood chip and mix, and the adjusting moisture content is 25%.With the vessel surface covered with plastic film, prick the hole ventilation, total petroleum hydrocarbons content is 804mg/kg in the soil after 25 ℃ were degraded 55 days down, degradation efficiency is 90.5%.
Embodiment 3
(1) will gather greasy dirt soil near the oil well, air-dry 20 days, remove volatile hydrocarbon and moisture content.
(2) rhodococcus erythropolis liquid being inserted the total petroleum hydrocarbon initial content is in the 6500mg/kg soil, and connecing the bacterium amount is 1.0 * 10 8Individual/g soil, do not add biosurfactant, add KNO 3And K 2HPO 4As nutritive salt, add H simultaneously 2O 210mg.
(3) add 10% wood chip and mix, and the adjusting moisture content is 25%.With the vessel surface covered with plastic film, prick the hole ventilation, total petroleum hydrocarbons content is 1235mg/kg in the soil after 20 ℃ were degraded 50 days down, degradation efficiency is 81%.

Claims (2)

1. the repairing method of microorganism of oil-polluted soils is characterized in that, concrete steps are as follows:
(1) will gather greasy dirt soil near the oil well, air-dry 20 ~ 30 days, remove volatile hydrocarbon and moisture content;
(2) rhodococcus erythropolis and verdigris first monad are cooperated Mixed Microbes in 1: 1 ratio, it is in 6500 ~ 8500mg/kg soil that bacterium liquid is inserted the total petroleum hydrocarbon initial content, and connecing the bacterium amount is 1.0 * 10 8~ 1.5 * 10 8Individual/g soil, add 1000 ~ 2000mg/kg biosurfactant again, add nutritive salt nitrogenous source and phosphorus source, add H simultaneously 2O 25 ~ 10mg;
(3) add 5 ~ 10% wood chips and mix, and the adjusting moisture content is 15 ~ 25%; With the vessel surface covered with plastic film, prick the hole ventilation, degraded 50 ~ 60 days down at 25 ~ 30 ℃.
2. by the repairing method of microorganism of the described oil-polluted soils of claim 1, it is characterized in that:
(1) will gather greasy dirt soil near the oil well, air-dry 25 days, remove volatile hydrocarbon and moisture content;
(2) rhodococcus erythropolis liquid and verdigris first monad cooperate Mixed Microbes in 1: 1 ratio, and inserting the total petroleum hydrocarbon initial content is in the 8460mg/kg soil, and connecing the bacterium amount is 1.5 * 10 8Individual/g soil, add the 2000mg/kg biosurfactant, add KNO 3And K 2HPO 4As nutritive salt nitrogenous source and phosphorus source, add H simultaneously 2O 27mg;
(3) add 8% wood chip and mix, and to regulate moisture content be 25%,, prick the hole ventilation the vessel surface covered with plastic film, 25 ℃ down degraded after 55 days in the soil total petroleum hydrocarbons content be 804mg/kg, degradation efficiency is 90.5%.
CN2007100558978A 2007-07-17 2007-07-17 Method for restoring petroleum polluted soil by microbe Expired - Fee Related CN101091957B (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102102088A (en) * 2010-12-10 2011-06-22 北京林业大学 Production method of petroleum hydrocarbon pollutant-degrading bacterium
CN111014282A (en) * 2019-12-31 2020-04-17 西安石油大学 Deep petroleum polluted soil simulation restoration device and application

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JPWO2010073976A1 (en) * 2008-12-24 2012-06-14 三菱瓦斯化学株式会社 Hydrogen peroxide solution with excellent stability
CN101691552B (en) * 2009-09-15 2012-05-30 北京大学 Bacterial strain capable of degrading petroleum hydrocarbon and application thereof
CN102125929B (en) 2010-01-18 2012-11-21 香港浸会大学 Biosurfactant and polycyclic aromatic hydrocarbon-degrading strain enhanced compositing treatment of contaminated soil
CN101890426B (en) * 2010-07-19 2011-11-30 南开大学 Method for restoring petroleum-polluted saline alkali soil by ryegrass and high efficiency microbes
CN102228900B (en) * 2011-05-18 2013-06-12 华北电力大学 In situ integrated restoring system and method of petroleum polluted soil
CN104056857B (en) * 2013-03-22 2017-10-27 东北林业大学 A kind of electronic auxiliary repairing method of microorganism of soil contaminated by crude oil
CN103992979B (en) * 2014-04-11 2017-02-15 东华大学 Bacterial capable of over-expressing membrane protein, and application thereof
CN105018390A (en) * 2015-08-05 2015-11-04 天津翌石开元科技发展有限公司 Rhodococcus erythropolis and application thereof
CN105776571B (en) * 2016-03-27 2019-07-02 广东创美达环保科技有限公司 A method of processing petroleum waste water
US10479711B2 (en) * 2016-05-05 2019-11-19 Remediation Products, Inc. Composition with a time release material for removing halogenated hydrocarbons from contaminated environments
CN106077075A (en) * 2016-06-16 2016-11-09 北京益博科环保科技有限公司 A kind of biological reinforced restorative procedure of gas station contaminated soil
CN106734181B (en) * 2016-12-02 2019-06-25 中国科学院新疆理化技术研究所 A kind of repairing method of microorganism of oil-polluted soils
CN108114976B (en) * 2017-12-19 2021-10-15 轻工业环境保护研究所 Method for restoring polluted soil
CN114472503A (en) * 2020-11-13 2022-05-13 新疆大学 Composite remediation method for soil polluted by leaky petroleum
CN115537353A (en) * 2022-09-15 2022-12-30 西安石油大学 Efficient composite degrading microbial inoculum and bioremediation process for oil-containing soil

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CN1565762A (en) * 2003-06-27 2005-01-19 中国科学院沈阳应用生态研究所 Biological method for restoring polluted soil by oil and PAH5
CN1672822A (en) * 2005-04-06 2005-09-28 东北师范大学 Prepn and usage of plant repairing body for contaminated soil
CN1718721A (en) * 2005-01-26 2006-01-11 清华大学 Method of treating oil contaminated soil and its special bacterin group

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CN1718721A (en) * 2005-01-26 2006-01-11 清华大学 Method of treating oil contaminated soil and its special bacterin group
CN1672822A (en) * 2005-04-06 2005-09-28 东北师范大学 Prepn and usage of plant repairing body for contaminated soil

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102102088A (en) * 2010-12-10 2011-06-22 北京林业大学 Production method of petroleum hydrocarbon pollutant-degrading bacterium
CN102102088B (en) * 2010-12-10 2012-08-29 北京林业大学 Production method of petroleum hydrocarbon pollutant-degrading bacterium
CN111014282A (en) * 2019-12-31 2020-04-17 西安石油大学 Deep petroleum polluted soil simulation restoration device and application
CN111014282B (en) * 2019-12-31 2021-09-03 西安石油大学 Deep petroleum polluted soil simulation restoration device and application

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Inventor after: Wang Xiaoyu

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