CN106190891B - Method based on sodium peroxydisulfate compound oxidation and the biological reinforced Combined Treatment soil with serious petroleum pollution of microbial flora or greasy filth - Google Patents

Method based on sodium peroxydisulfate compound oxidation and the biological reinforced Combined Treatment soil with serious petroleum pollution of microbial flora or greasy filth Download PDF

Info

Publication number
CN106190891B
CN106190891B CN201610541245.4A CN201610541245A CN106190891B CN 106190891 B CN106190891 B CN 106190891B CN 201610541245 A CN201610541245 A CN 201610541245A CN 106190891 B CN106190891 B CN 106190891B
Authority
CN
China
Prior art keywords
soil
greasy filth
bacillus
sodium peroxydisulfate
bacterium
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
Application number
CN201610541245.4A
Other languages
Chinese (zh)
Other versions
CN106190891A (en
Inventor
马小魁
毛东霞
周波
李郁
郭丹丹
李亭亭
马瑶
宋双红
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.)
Shaanxi Normal University
Original Assignee
Shaanxi Normal University
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 Shaanxi Normal University filed Critical Shaanxi Normal University
Priority to CN201610541245.4A priority Critical patent/CN106190891B/en
Publication of CN106190891A publication Critical patent/CN106190891A/en
Application granted granted Critical
Publication of CN106190891B publication Critical patent/CN106190891B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12NMICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
    • C12N1/00Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
    • C12N1/20Bacteria; Culture media therefor
    • 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
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C1/00Reclamation of contaminated soil
    • B09C1/10Reclamation of contaminated soil microbiologically, biologically or by using enzymes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C1/00Reclamation of contaminated soil
    • B09C1/10Reclamation of contaminated soil microbiologically, biologically or by using enzymes
    • B09C1/105Reclamation of contaminated soil microbiologically, biologically or by using enzymes using fungi or plants
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • C02F3/344Biological treatment of water, waste water, or sewage characterised by the microorganisms used for digestion of mineral oil
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • C02F3/347Use of yeasts or fungi
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12NMICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
    • C12N1/00Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
    • C12N1/14Fungi; Culture media therefor
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C2101/00In situ
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/10Nature of the water, waste water, sewage or sludge to be treated from quarries or from mining activities
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/34Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
    • C02F2103/36Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the manufacture of organic compounds
    • C02F2103/365Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the manufacture of organic compounds from petrochemical industry (e.g. refineries)

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Microbiology (AREA)
  • Chemical & Material Sciences (AREA)
  • Health & Medical Sciences (AREA)
  • Organic Chemistry (AREA)
  • Biotechnology (AREA)
  • Environmental & Geological Engineering (AREA)
  • Mycology (AREA)
  • General Health & Medical Sciences (AREA)
  • Zoology (AREA)
  • Biomedical Technology (AREA)
  • Bioinformatics & Cheminformatics (AREA)
  • Genetics & Genomics (AREA)
  • Wood Science & Technology (AREA)
  • Water Supply & Treatment (AREA)
  • Soil Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Tropical Medicine & Parasitology (AREA)
  • Biochemistry (AREA)
  • General Engineering & Computer Science (AREA)
  • Virology (AREA)
  • Medicinal Chemistry (AREA)
  • Botany (AREA)
  • Molecular Biology (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Fertilizers (AREA)

Abstract

The invention discloses a kind of methods based on sodium peroxydisulfate compound oxidation and the biological reinforced Combined Treatment soil with serious petroleum pollution of microbial flora or greasy filth, it is used cooperatively first with sodium peroxydisulfate compound as oxidant and surfactant and oxidation processes is carried out to contaminated soil or greasy filth, access the mixed bacterial of bacillus (Bacillus sp.) and branch acremonium bacterium (Acremonium sp.Y0997) or Phanerochaete chrysosporium (Phanerochaete sp.F0996) twice in succession later, combined by chemical oxidation with fungi-bacteria flora biological sequence reinforcing and reinforcing Combined Treatment is carried out to soil or greasy filth, it has been remarkably improved the degradation efficiency of soil with serious petroleum pollution or greasy filth, and it is substantially shorter repairing efficiency.

Description

Based on the oxidation of sodium peroxydisulfate compound and the biological reinforced Combined Treatment weight of microbial flora Spend the method for oil-polluted soils or greasy filth
Technical field
The invention belongs to soil with serious petroleum pollution or the chemistry and technical field of biological remediation of greasy filth, and in particular to oil Field mining area utilizes chemical oxidation and the biological reinforced reinforcing Combined Treatment soil with serious petroleum pollution of fungi-bacteria flora or greasy filth Method.
Technical background
Currently, oil-polluted soils range constantly expands with the development of domestic and international petroleum industry.For petroleum wastewater Dye soil is handled, and is made it achieve the effect that restore to utilize in a relatively short period of time, is in oil-polluted soils governance process Urgent problem to be solved.Which method optimum of processing to(for) pollutant selects, in addition to consider handling pollutant location Point, amount of pollutant number, outside the technical factors such as length of the quality for the treatment of effect, the length of required time and processing, processing The height of expense is a highly important factor.
In recent years, bioremediation technology has at home and abroad all obtained faster development, and a batch has special physiological biochemistry function Plant, the microorganism of energy are come into being, and the further application and development of bioremediation technology have been pushed.In oil-polluted soils Governance process in, on the one hand further to improve bioremediation technology, make its maturing and systematization;On the other hand it is noted that And the combination of conventional method plays respective advantage.
Current relatively simple to the means of the processing of oil pollution both at home and abroad, the single recovery technique mainly used, it is single One biological prosthetic or single chemical method.Single bioremediation technology is although environmentally friendly, and biology is degeneration-resistant Property environment in laundering period it is often longer, therefore in Polluted area processing urgently to be resolved and bad.It therefore is that can make to repair function Effect is more satisfied, and reparation result is more thorough, and the chemical repair method rapidly reacted is essential.Skill is repaired in chemical treatment Art success application first consists in the selection of suitable inorganic agent.Currently used chemical treatments have hydrogen peroxide, Gao Meng Hydrochlorate, Fenton reagent, modified Fenton reaction and activation persulfate etc..In addition, Watts etc. (1999) reports very strong place Manage bar part, excessive H2O2The desorption and processing that the organic pollutant of absorption can be improved by generating other free radical, Dadkhah&Akgerman (2006) points out to use subcritical water as removal medium and crosses processing hydrogen as inorganic agent, and 30 points There is no PAHs that can be detected in liquid after clock experiment.External existing company, as REGEBESIS and I-ROX is also being concentrated on The research of chemical treatment degradation underground water pollution.But chemical treatment method also has its limitation, such as in processing degradation process In, inorganic agent can handle other organic matters in soil and change the adsorption structure in soil and biology can Usability is unfavorable for the growth of plant and microorganism, cannot effectively be used in combination with bioremediation technology.
For the efficiency for further increasing reparation, the engagement technique between chemical oxidation and biological treatment, this hair are solved the problems, such as It is bright to propose a kind of joint processing technology based on the biological reinforced strategy of sodium peroxydisulfate oxidation processes and flora, to severe stone Soil contaminated by crude oil or greasy filth are efficiently treated through.
Summary of the invention
It is biological reinforced based on the oxidation of sodium peroxydisulfate compound and microbial flora that the purpose of the present invention is to provide one kind The method for closing processing soil with serious petroleum pollution or greasy filth, this method can improve soil with serious petroleum pollution or oil extremely significantly The treatment effeciency of mud, and process cycle can be greatly shortened, combine sodium peroxydisulfate oxidation processes substrate it is selectively low, it is efficient, Period is short and the biological reinforced processing of flora is mild, the environment amenable plurality of advantages of converted product, in contaminated soil or can contain Greasy dirt sludge-polluted scene original position or dystopy processing soil with serious petroleum pollution or greasy filth.
Biological reinforced combination treatment method according to the present invention is using bacillus (Bacillus sp.) and branch top Fungi-bacteria flora solid of spore mould (Acremonium sp.) or Phanerochaete chrysosporium (Phanerochaete sp.) Microbial inoculum accesses in soil with serious petroleum pollution or greasy filth.
Bacterium according to the present invention is respectively bacillus, branch acremonium bacterium and Phanerochaete chrysosporium, in which: gemma bar Bacterium Bacillus sp., bacterial strain deposit number CCTCC NO:AB 2014248, belongs to known solid fungicide, and the bacterium bacterium colony is in milky white Color, bacterium colony is round, and surface is smooth, raised, neat in edge, and back side color is consistent with front, non-pigment distribution.Branch acremonium bacterium Acremonium sp.Y0997, bacterial strain deposit number are CCTCC NO:M 2016117, and depositary institution is that Chinese Typical Representative culture is protected Hiding center, address: Wuhan, China Wuhan University, postcode: 430072, preservation date is on March 14th, 2016, and the bacterium bacterium colony is in white Color, bacterium colony is round, back side cream color to ochre yellow, hyphae colorless, and smooth and tool diaphragm, sporangiophore are long directly from mycelia Out, tapered more Dan Sheng, conidium is colourless, smooth, forms tufted or chain, long spindle is pointed at both ends, has no thick wall spore Son.Phanerochaete chrysosporium Phanerochaete sp.F0996, bacterial strain deposit number are CCTCC NO:M 2016116, preservation list Position is China typical culture collection center, address: Wuhan, China Wuhan University, postcode: 430072, preservation date is 2016 March 14, the bacterium bacteria colony white, round, the back side is colourless, the only a small amount of protrusion of bacterium colony;Mycelia is colourless, fluffy flocculence, with The extension of incubation time, villiform protrusion gradually flatten, mycelia disappear, formed aleuriospore.
To achieve the goals above, the technical solution adopted in the present invention comprises the steps of:
(1) it acquires soil with serious petroleum pollution or greasy filth is placed in processing pond, broken into pieces, mixed, or directly will pollution The soil with serious petroleum pollution or greasy filth at scene are broken into pieces, are mixed;
(2) soil handled through step (1) is added in the ratio of 8~15g/kg using sodium peroxydisulfate compound as oxidant Or in greasy filth, and the moisture content for adding water to soil or greasy filth mixes, oxidation processes 10~20 days up to 15~30%;
(3) cultured bacillus and branch top born of the same parents mould are respectively connected into step (2) treated soil or greasy filth Mix bacterium agent or bacillus and Phanerochaete chrysosporium mix bacterium agent, bacillus and branch acremonium bacterium or yellow archespore The inoculum concentration of the flat lead fungi of hair is 15~25g/kg, adds organic fertilizer, and the additive amount of organic fertilizer is 800~1200mg/ Kg is mixed, the surface of contaminated soil or greasy filth is covered with plastic film, is ventilated, and the moisture content of soil or greasy filth is maintained to stablize, At 15~35 DEG C, in-situ processing 10~20 days;
(4) the cultured bacillus of equivalent and branch top born of the same parents are accessed again into step (3) treated soil or greasy filth The mix bacterium agent of mould or the mix bacterium agent of bacillus and Phanerochaete chrysosporium repeat the operation of step (3), 15~ At 35 DEG C, in-situ processing 20~30 days, completion processing.
Above-mentioned sodium peroxydisulfate compound is accessed in the soil or greasy filth handled through step (1) in the ratio of 8~15g/kg, then Biology or nontoxic surfactants are added, the additive amount of surfactant is 1200~1600mg/kg, and adds water to soil or oil The moisture content of mud mixes, oxidation processes 10~20 days up to 15~30%;
Above-mentioned sodium peroxydisulfate compound is mixed by sodium peroxydisulfate, calper calcium peroxide and ferrous sulfate with the molar ratio of 5:0.5:2.5 Conjunction is made.
The entitled Acremonium sp.Y0997 of above-mentioned branch acremonium bacterium, bacterial strain deposit number are CCTCC NO:M 2016117, the deposit date is on March 14th, 2016, and depositary institution is China typical culture collection center;Yellow archespore Mao Pingge The entitled Phanerochaete sp.F0996 of bacterium, bacterial strain deposit number are CCTCC NO:M 2016116, during depositary institution is State's Type Tissue Collection, preservation date are on March 14th, 2016.
The viable bacteria content of above-mentioned bacillus is 4.0 × 109~6.0 × 109The viable bacteria content of CFU/g, branch acremonium bacterium is 7.2×109~8.5 × 109CFU/g, the viable bacteria content of Phanerochaete chrysosporium are 7.2 × 109~9.0 × 109CFU/g。
The total petroleum hydrocarbon initial content of above-mentioned soil with serious petroleum pollution or greasy filth is 100000~170000mg/kg soil Or greasy filth.
The present invention is based on the oxidations of sodium peroxydisulfate compound and the biological reinforced Combined Treatment serious petroleum pollution of microbial flora The method of soil or greasy filth is first to connect twice in succession again after oxidant and surfactant cooperation carry out chemical oxidation treatment The mixed bacterial for entering bacillus and branch acremonium bacterium or Phanerochaete chrysosporium carries out the biological reinforced reparation of sequence, by chemical oxygen Change technology is capable of the degradation effect of the raising TPH on extremely significant ground in conjunction with the biological reinforced recovery technique of fungi-bacteria flora sequence Rate, and substantially reduce repairing efficiency, combine that sodium peroxydisulfate oxidation processes substrate is selectively low, efficient, period is short and Flora is biological reinforced to handle mild, the environment amenable plurality of advantages of converted product, can pollute in contaminated soil or oily sludge Live original position or dystopy processing soil with serious petroleum pollution or greasy filth.Serious petroleum pollution to crude quality at concentrations up to 17% The treatment effect of soil or greasy filth is obvious, and test result shows: after processing 10~20 days, TPH degradation efficiency in soil or greasy filth It is 30%~50%, 35% or more has been reached to the degradation efficiency of wherein light chain and heavy chain component, respectively 38.53 ± 1.06%, 42.78 ± 1.45%, pass through subsequent bacillus sp.'s and branch acremonium bacterium Acremonium sp. Flora is by a definite date after processing in 35~50 days, and TPH degradation efficiency has reached 86%~95% in soil or greasy filth, flora of the invention Growth is stablized, and branch acremonium bacterium and Phanerochaete chrysosporium are preferable to the tolerance of outdoor elements at the scene, survival rate It is higher, further it is proposed that technical system can apply to completely petroleum-type compound pollution a variety of media such as Polluted Soil The production waste or petroleum wastewater etc. of earth or oily sludge and shale gas collection site, and had in oil producing operation area On-site verification, it is reliable and stable, also can operate with petroleum-type compound pollution a variety of media such as contaminated soil or pollutant effluents with And the production waste or petroleum wastewater etc. of shale gas collection site.
Detailed description of the invention
Fig. 1 is the bacterium colony figure of branch acremonium bacterium (Acremonium sp.Y0997).
Fig. 2 is the shape appearance figure of Phanerochaete chrysosporium (Phanerochaete sp.F0996).
Fig. 3 is the internal standard method for gas chromatography analysis map for handling petroleum the hydrocarbon component in 15 days blank example soil.
Fig. 4 is the internal standard method for gas chromatography analysis of petroleum the hydrocarbon component in 15 days 1 soil of embodiment of chemical oxidation treatment Map.
Fig. 5 is the removal efficiency result of light chain and heavy chain component in 15 days 1 soil of embodiment of chemical oxidation treatment.
Fig. 6 is TPH removal efficiency comparing result in 60 days blank examples of processing and comparative example and 1 soil of embodiment.
Specific embodiment
Technical solution of the present invention is further described now in conjunction with test and embodiment, but the present invention is not limited only to Embodiment disclosed below.
Embodiment 1
Now with bacillus, (Bacillus sp. is preserved in China typical culture collection center, bacterial strain deposit number CCTCC NO:AB2014248) and branch acremonium bacterium (Acremonium sp.Y0997, is preserved in China typical culture collection Center, bacterial strain deposit number be CCTCC NO:M 2016117, preservation date is on March 14th, 2016) solid fungicide be flora Combination, using sodium peroxydisulfate compound as chemical oxidizing agent, combines and handles soil with serious petroleum pollution, by following steps group At:
(1) soil with serious petroleum pollution that the total petroleum hydrocarbon initial content near oil well is 162240mg/kg is acquired to be placed in It in processing pond, is broken into pieces, partial size is 30~40mm or so, is mixed;
(2) oxidant sodium peroxydisulfate compound is accessed in the soil handled through step (1) in the ratio of 10g/kg, adds water To the moisture content of soil up to 25%, mix, oxidation processes 15 days, which was by sodium peroxydisulfate, calper calcium peroxide It is mixed with ferrous sulfate with the molar ratio of 5:0.5:2.5;
(3) cultured bacillus (Bacillus sp.) and branch acremonium bacterium (Acremonium sp.) are accessed into weight It spends in oil-polluted soils, the inoculum concentration of bacillus is 20g/kg soil (its solid fungicide viable bacteria content: 5.3 × 109CFU/ G), the inoculum concentration of branch acremonium bacterium is 20g/kg soil (its solid fungicide viable bacteria content: 8.0 × 109CFU/g), according still further to Organic fertilizer is added in the amount of 1000mg/kg (soil), mixes, and maintains the moisture content of soil to stablize, the surface of processing pond is moulded Expect that film covering, ventilation maintain the moisture content of soil to stablize, at 25 DEG C, in-situ processing 15 days;
(4) the cultured bacillus of equivalent and branch acremonium bacterium are accessed again into step (3) treated soil, weight The operation of multiple step (3), at 25 DEG C, in-situ processing 30 days, completion processing, the degradation rate of TPH reached 86.96%.
The 18SrDNA sequence of above-mentioned branch acremonium bacterium (Acremonium sp.Y0997) are as follows:
The bacterium bacterium colony is white, and bacterium colony is round, back side cream color to ochre yellow, hyphae colorless, smooth and tool diaphragm, spore Upright connect of capsule grows from mycelia, and tapered more Dan Sheng, conidium is colourless, smooth, formation tufted or chain, long spindle, It is pointed at both ends, have no chlamydospore, pattern is referring to Fig. 1.
Embodiment 2
Now with Phanerochaete chrysosporium, (Phanerochaete sp.F0996, is preserved in China typical culture collection The heart, bacterial strain deposit number CCTCC NO:M 2016116, preservation date are on March 14th, 2016) solid fungicide be flora composition, Using sodium peroxydisulfate compound as chemical oxidizing agent, combine and soil with serious petroleum pollution handled, comprises the steps of:
(1) soil with serious petroleum pollution that the total petroleum hydrocarbon initial content near oil well is 170000mg/kg is acquired to be placed in It in processing pond, is broken into pieces, partial size is 30~40mm or so, is mixed;
(2) oxidant sodium peroxydisulfate compound is accessed in the soil handled through step (1) in the ratio of 8g/kg, adds water To the moisture content of soil up to 15%, mix, oxidation processes 20 days, sodium peroxydisulfate compound used was by sodium peroxydisulfate, peroxidating Calcium and ferrous sulfate are mixed with the molar ratio of 5:0.5:2.5;
(3) by cultured bacillus (Bacillus sp.) and Phanerochaete chrysosporium (Phanerochaete Sp.F0996 it) accesses in soil with serious petroleum pollution, the inoculum concentration of bacillus is that (its solid fungicide viable bacteria contains 15g/kg soil Amount: 4.0 × 109CFU/g), the inoculum concentration of Phanerochaete chrysosporium be 15g/kg soil (its solid fungicide viable bacteria content: 7.5 × 109CFU/g), organic fertilizer is added according still further to the amount of 800mg/kg (soil), mixes, maintain the moisture content of soil to stablize, will locate The surface in reason pond is covered with plastic film, is ventilated, and the moisture content of soil is maintained to stablize, at 15 DEG C, in-situ processing 20 days;
(4) the cultured bacillus of equivalent and yellow archespore Mao Pingge are accessed again into step (3) treated soil The mix bacterium agent of bacterium repeats the operation of step (3), and at 15 DEG C, in-situ processing 30 days, completion processing, the degradation rate of TPH reached 85.25%.
Above-mentioned Phanerochaete chrysosporium Phanerochaete sp.F0996, bacterial strain deposit number are CCTCC NO:M 2016116, depositary institution is China typical culture collection center, and preservation date is on March 14th, 2016,18SrDNA sequence It is classified as:
The bacterium bacteria colony white, round, the back side is colourless, the only a small amount of protrusion of bacterium colony;Mycelia is colourless, fluffy flocculence, with The extension of incubation time, villiform protrusion gradually flatten, mycelia disappear, formed aleuriospore, referring to fig. 2.
Embodiment 3
Using sodium peroxydisulfate compound as chemical oxidizing agent, combine bacillus and branch acremonium bacterium mixed bacterial to severe stone Oily pollution greasy filth carries out reinforcing Combined Treatment, comprises the steps of:
(1) the serious petroleum pollution greasy filth that the total petroleum hydrocarbon initial content near oil well is 100000mg/kg is acquired to be placed in It in processing pond, is broken into pieces, partial size is 30~40mm or so, is mixed;
(2) oxidant sodium peroxydisulfate compound is accessed in the greasy filth handled through step (1) in the ratio of 12g/kg, over cure Sour sodium compound is mixed by sodium peroxydisulfate, calper calcium peroxide and ferrous sulfate with the molar ratio of 5:0.5:2.5, according still further to Heavy oil cleaning agent KD-L315 is added as surfactant in the additive amount of 1200mg/kg (greasy filth), and adds water to the aqueous of greasy filth Rate mixes, oxidation processes 10 days up to 30%;
(3) cultured bacillus (Bacillus sp.) and branch acremonium bacterium (Acremonium sp.) are accessed into weight It spends in oil pollution greasy filth, the inoculum concentration of bacillus is 25g/kg greasy filth (its solid fungicide viable bacteria content: 6.0 × 109CFU/ G), the inoculum concentration of branch acremonium bacterium is 25g/kg greasy filth (its solid fungicide viable bacteria content: 8.5 × 109CFU/g), according still further to Organic fertilizer is added in the amount of 1200mg/kg (greasy filth), mixes, and maintains the moisture content of greasy filth to stablize, the surface of processing pond is moulded Expect that film covering, ventilation maintain the moisture content of greasy filth to stablize, at 35 DEG C, in-situ processing 10 days;
(4) the cultured bacillus of equivalent and branch acremonium bacterium are accessed again into step (3) treated greasy filth, weight The operation of multiple step (3), at 35 DEG C, in-situ processing 20 days, completion processing, the degradation rate of TPH reached 95.01%.
Embodiment 4
Using sodium peroxydisulfate compound as chemical oxidizing agent, combine bacillus and Phanerochaete chrysosporium mixed bacterial counterweight Degree oil pollution greasy filth carries out reinforcing Combined Treatment, comprises the steps of:
(1) the serious petroleum pollution greasy filth that the total petroleum hydrocarbon initial content near oil well is 120000mg/kg is acquired to be placed in It in processing pond, is broken into pieces, partial size is 30~40mm or so, is mixed;
(2) oxidant sodium peroxydisulfate compound is accessed in the greasy filth handled through step (1) in the ratio of 15g/kg, over cure Sour sodium compound is mixed by sodium peroxydisulfate, calper calcium peroxide and ferrous sulfate with the molar ratio of 5:0.5:2.5, according still further to The additive amount of 1600mg/kg (greasy filth) be added heavy oil cleaning agent KD-L315 as surfactant or other it is commercially available biological or Nontoxic surfactants, and the moisture content for adding water to greasy filth mixes, oxidation processes 10 days up to 30%;
(3) by cultured bacillus (Bacillus sp.) and Phanerochaete chrysosporium (Phanerochaete Sp. in mix bacterium agent access serious petroleum pollution greasy filth), the inoculum concentration of bacillus is 25g/kg greasy filth (its solid fungicide Viable bacteria content: 5.0 × 109CFU/g), the inoculum concentration of Phanerochaete chrysosporium is that (its solid fungicide viable bacteria contains 25g/kg greasy filth Amount: 9.0 × 109CFU/g), organic fertilizer is added according still further to the amount of 1200mg/kg (greasy filth), mixes, maintains the moisture content of greasy filth Stablize, the surface of processing pond is covered with plastic film, ventilate, the moisture content of greasy filth is maintained to stablize, at 35 DEG C, in-situ processing 10 days;
(4) the cultured bacillus of equivalent and yellow archespore Mao Pingge are accessed again into step (3) treated greasy filth Bacterium repeats the operation of step (3), and at 35 DEG C, in-situ processing 20 days, completion processing, the degradation rate of TPH reached 93.31%.
Method of the invention is applicable to processing soil with serious petroleum pollution and greasy filth, and it is existing can also directly to handle pollution The soil with serious petroleum pollution or greasy filth of field, can obtain good treatment effect.
Above-mentioned branch top born of the same parents mould can be replaced mutually with Phanerochaete chrysosporium, be mixed to form very with bacillus Bacterium-bacterium mix bacterium agent has a preferable effect to above-mentioned soil with serious petroleum pollution and greasy filth, especially with oxidant oxygen Change Combined Treatment.
In order to verify technical effect of the invention, applicant has done a large amount of experiment, while also using blank assay as ginseng According to, degradation effect of the invention is verified, specific as follows:
Comparative example
(1) total petroleum hydrocarbon initial content is that 162240mg/kg soil with serious petroleum pollution is placed in processing pond, is struck It is broken, it mixes;
(2) identical as (3) the step of embodiment 1.
(3) identical as (4) the step of embodiment 1.
Blank example:
(1) identical as comparative example 1;
(2) organic fertilizer and surface-active is added into the contaminated soil that total petroleum hydrocarbon initial content is 162240mg/kg Agent, and the moisture content for adding water to soil is mixed up to 25%, at 15~35 DEG C, in-situ processing 60 days, completion processing.
Total petroleum hydrocarbon component carries out gas-chromatography and mass spectrum in soil after handling 15 days above-mentioned blank example and embodiment 1 Combination detection, as a result shown in following Fig. 3 and Fig. 4.
By in Fig. 3 and 4 the results show that compared with blank example, it is each in soil after sodium peroxydisulfate compound oxidation processes Petroleum the hydrocarbon component has obvious degradation effect, and carries out to the removal efficiency of light chain and heavy chain component in soil after oxidation processes It calculates, as a result as shown in Figure 5.As shown, light chain and heavy chain component after sodium peroxydisulfate compound oxidation processes, in soil Removal efficiency respectively reached 38.53 ± 1.06%, 42.78 ± 1.45%.
The degradation situation of total petroleum hydrocarbon in soil after handled by above-mentioned comparative example and blank example is detected, and with reality It applies example 1 to be compared, as a result as shown in the following table 1 and Fig. 6.
Table 1 is the comparing result of TPH content and embodiment 1 in comparative example and blank example treated soil
By table 1 and Fig. 6 it is found that comparative example and blank example handle 60 days after soil in TPH content and embodiment 1 comparison The result shows that the TPH removal efficiency that improves in soil extremely significant using the embodiment 1 of chemical oxidation pre-treatment, with comparison Example is compared, and the TPH removal efficiency of embodiment 1 improves about 22.54%.
It is also handled with greasy filth of the identical method to serious petroleum pollution, can also reach above-mentioned identical processing effect Fruit.
Test result shows the present invention using chemical oxidation and the biological reinforced comprehensive in-situ processing weight of fungi-bacteria flora Oil-polluted soils or greasy filth are spent, the degradation efficiency of total petroleum hydrocarbon in soil or greasy filth can be improved extremely significantly.

Claims (2)

1. one kind is based on the oxidation of sodium peroxydisulfate compound and the biological reinforced Combined Treatment soil with serious petroleum pollution of microbial flora Or the method for greasy filth, it is characterised in that comprise the steps of:
(1) it acquires soil with serious petroleum pollution or greasy filth is placed in processing pond, broken into pieces, mixed, or directly will pollution scene Soil with serious petroleum pollution or greasy filth break into pieces, mix;
(2) soil or oil handled through step (1) is added in the ratio of 8 ~ 15 g/kg using sodium peroxydisulfate compound as oxidant In mud, surfactant is added, the additive amount of surfactant is 1200 ~ 1600 mg/kg, and adds water to soil or greasy filth Moisture content up to 15 ~ 30%, mix, oxidation processes 10 ~ 20 days;
Above-mentioned sodium peroxydisulfate compound is mixed by sodium peroxydisulfate, calper calcium peroxide and ferrous sulfate with the molar ratio of 5:0.5:2.5 It is made;
(3) be respectively connected into step (2) treated soil or greasy filth cultured bacillus (BacillusSp.) with Branch top born of the same parents mould (AcremoniumSp. mix bacterium agent or bacillus and Phanerochaete chrysosporium) (PhanerochaeteSp. the inoculum concentration of mix bacterium agent), bacillus and branch acremonium bacterium or Phanerochaete chrysosporium is equal For 15 ~ 25 g/kg, organic fertilizer is added, the additive amount of organic fertilizer is 800 ~ 1200 mg/kg, is mixed, by contaminated soil Or the surface of greasy filth is covered with plastic film, ventilation, and the moisture content of soil or greasy filth is maintained to stablize, at 15 ~ 35 DEG C, at scene Reason 10 ~ 20 days;
(4) the cultured bacillus of equivalent and branch top born of the same parents mould are accessed again into step (3) treated soil or greasy filth Mix bacterium agent or bacillus and Phanerochaete chrysosporium mix bacterium agent, repeat step (3) operation, at 15 ~ 35 DEG C Under, in-situ processing 20 ~ 30 days, completion processing;
Above-mentioned Phanerochaete chrysosporium (PhanerochaeteSp. entitled F0996), in preservation on March 14 in 2016 In China typical culture collection center, deposit number is CCTCC NO:M 2016116, and preservation address is that Wuhan City, Hubei Province is military Chinese university;Branch acremonium bacterium (AcremoniumSp. entitled Y0997) is preserved in Chinese Typical Representative on March 14th, 2016 Culture collection, deposit number are CCTCC NO:M 2016117, and preservation address is Wuhan City, Hubei Province Wuhan University;Bud Spore bacillus (BacillusSp. deposit number) is CCTCC NO: AB 2014248.
2. according to claim 1 based on the oxidation of sodium peroxydisulfate compound and the biological reinforced Combined Treatment weight of microbial flora Spend the method for oil-polluted soils or greasy filth, it is characterised in that: the viable bacteria content of the bacillus is 4.0 × 109~ 6.0× 109CFU/g, the viable bacteria content of branch acremonium bacterium are 7.2 × 109 ~8.5×109The viable bacteria of CFU/g, Phanerochaete chrysosporium contain Amount is 7.2 × 109 ~9.0×109 CFU/g。
CN201610541245.4A 2016-07-11 2016-07-11 Method based on sodium peroxydisulfate compound oxidation and the biological reinforced Combined Treatment soil with serious petroleum pollution of microbial flora or greasy filth Active CN106190891B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610541245.4A CN106190891B (en) 2016-07-11 2016-07-11 Method based on sodium peroxydisulfate compound oxidation and the biological reinforced Combined Treatment soil with serious petroleum pollution of microbial flora or greasy filth

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610541245.4A CN106190891B (en) 2016-07-11 2016-07-11 Method based on sodium peroxydisulfate compound oxidation and the biological reinforced Combined Treatment soil with serious petroleum pollution of microbial flora or greasy filth

Publications (2)

Publication Number Publication Date
CN106190891A CN106190891A (en) 2016-12-07
CN106190891B true CN106190891B (en) 2019-10-25

Family

ID=57473087

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610541245.4A Active CN106190891B (en) 2016-07-11 2016-07-11 Method based on sodium peroxydisulfate compound oxidation and the biological reinforced Combined Treatment soil with serious petroleum pollution of microbial flora or greasy filth

Country Status (1)

Country Link
CN (1) CN106190891B (en)

Families Citing this family (15)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106811205B (en) * 2016-12-21 2020-04-10 中国石油天然气集团公司 Method for restoring petroleum hydrocarbon polluted soil by persulfate coupled indigenous microorganism stimulation
CN106623405A (en) * 2016-12-22 2017-05-10 常州大学 Method for remediation of benzene hexachloride contaminated soil by Fe (II) / CaO2
CN106734164A (en) * 2016-12-22 2017-05-31 常州大学 A kind of microwave reinforced nanometer Fe3O4/Na2CO4The method for repairing PAEs contaminated soils
CN107214189A (en) * 2017-07-19 2017-09-29 河北煜环环保科技有限公司 A kind of organic material contaminated soil renovation technique
CN108580539B (en) * 2018-04-18 2021-02-05 浙江大学 Method for restoring organic contaminated soil by coupling chemical oxidation with microorganisms
CN108435786A (en) * 2018-05-07 2018-08-24 句容宇发农业发展有限公司 A method of repairing pesticide contaminated soil
CN108941191A (en) * 2018-07-03 2018-12-07 上海松沅环境修复技术有限公司 A kind of repairing method of microorganism of oil-polluted soils
CN108892353A (en) * 2018-09-19 2018-11-27 新疆科力新技术发展股份有限公司 Oil field mining liquid central treating station process for treating oil-containing sludge and device
CN109095740A (en) * 2018-10-15 2018-12-28 中石化石油工程技术服务有限公司 Oily sludge method for innocent treatment
CN109759431A (en) * 2019-01-25 2019-05-17 湖南新九方科技有限公司 A kind of restorative procedure of gas station's contaminated site
CN111922065A (en) * 2020-07-31 2020-11-13 中冶华天工程技术有限公司 Method for restoring organic contaminated soil by combining chemical oxidation with microorganisms
USD1026013S1 (en) * 2021-08-11 2024-05-07 Beijing Kuaimajiabian Technology Co., Ltd. Display screen or portion thereof with an animated graphical user interface
CN113770155B (en) * 2021-08-20 2022-12-02 鄂尔多斯市昊鑫绿科环境工程有限公司 High-temperature oxidation treatment method for drilling solid waste of oil and gas field
CN113787093B (en) * 2021-09-14 2022-09-02 中国科学院武汉岩土力学研究所 Method for repairing organic polluted soil by activating sodium persulfate through carbide slag loaded with bacillus
CN115572031A (en) * 2022-10-28 2023-01-06 中南大学 Method for treating oily sludge by combining biological treatment and chemical treatment

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102794296A (en) * 2012-08-01 2012-11-28 中国石油天然气股份有限公司 Complex microbial inoculant for restoring petroleum-contaminated soil in loess highlands and restoring method thereof
CN104031870A (en) * 2014-06-24 2014-09-10 西北民族大学 Microbial compound bacterial agent and soil combined remediation agent prepared from microbial compound bacterial agent and application of microbial compound bacterial agent and soil combined remediation agent
CN105170644A (en) * 2015-10-30 2015-12-23 李磊 Bioremediation method for petroleum-polluted soil

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102794296A (en) * 2012-08-01 2012-11-28 中国石油天然气股份有限公司 Complex microbial inoculant for restoring petroleum-contaminated soil in loess highlands and restoring method thereof
CN104031870A (en) * 2014-06-24 2014-09-10 西北民族大学 Microbial compound bacterial agent and soil combined remediation agent prepared from microbial compound bacterial agent and application of microbial compound bacterial agent and soil combined remediation agent
CN105170644A (en) * 2015-10-30 2015-12-23 李磊 Bioremediation method for petroleum-polluted soil

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
Bioaugmentation of soil contaminated with high-level crude oil through inoculation with mixed cultures including Acremonium sp.;Xiao-Kui Ma et al.;《Biodegradation》;20150501;259–269 *
CaO2/Fe2+活化过硫酸钠对石油类污染土壤的修复效果;吴昊 等;《环境科学》;20160430;第35卷(第4期);623-628 *
活化过硫酸钠原位修复石油类污染土壤研究进展;吴昊 等;《环境化学》;20151130;第34卷(第11期);2085-2095 *
黄孢原毛平革菌对土壤中石油的降解研究;谭丽泉 等;《安徽农业科学》;20111231;第39卷(第35期);21975-21978 *

Also Published As

Publication number Publication date
CN106190891A (en) 2016-12-07

Similar Documents

Publication Publication Date Title
CN106190891B (en) Method based on sodium peroxydisulfate compound oxidation and the biological reinforced Combined Treatment soil with serious petroleum pollution of microbial flora or greasy filth
CN106077076B (en) A method of based on SODIUM PERCARBONATE oxidation and microbial augmentation integrated treatment soil with serious petroleum pollution or greasy filth
CN109570220B (en) Method for restoring arsenic-polluted soil by bacteria-induced active iron manganese oxide under aerobic/microaerobic conditions
CN110283772A (en) A kind of preparation method of functional flora that repairing petroleum hydrocarbon contaminated soil and underground water
CN106119158B (en) A kind of petroleum hydrocarbon degradation bacterial strain, petroleum hydrocarbon degradation microbial inoculum and the preparation method and application thereof
CN108130299B (en) Microbial strain for degrading petroleum hydrocarbon and combined repairing agent
CN104745511B (en) Composite bacteria agent for repairing heavy oil pollution coastline and preparation method and application
CN105032908B (en) The device and process of a kind of renovation of organic pollution soil and underground water
CN103333826B (en) Manganese oxidizing bacteria and application thereof
CN103224282A (en) Method and special equipment for treating oil field wastewater
CN104438283B (en) A kind of method utilizing microorganism to accelerate aerobic degradation urban solid garbage refuse
CN103408002A (en) Microbial reduction of graphene oxide and preparation method for graphene
CN103484447A (en) Preparation method and application of petroleum degrading enzyme preparation
CN104649848A (en) Solid bacterial fertilizer for remedying petroleum polluted saline alkali soil and preparation method of solid bacterial fertilizer
CN110116132A (en) A kind of method that charcoal base composite bacteria agent strengthens remedying oil-polluted soils
CN105820963B (en) Phanerochaete chrysosporium and its application
CN109665633A (en) A kind of preparation method of functional flora that repairing phenols contaminated soil and underground water
CN108687131A (en) Chemical pollution site remediation method
CN108114978B (en) A kind of method of the efficient rehabilitating soil of chemistry-microorganism
CN113695369A (en) Method for in-situ remediation of petroleum hydrocarbon contaminated soil through multi-technology coupling
CN109455891A (en) A kind of compound bio preparation for repairing for oily sludge
CN104307870A (en) Bioslurry repair method for poly brominated diphenyl ethers polluted soil, and special equipment
CN106082447A (en) A kind of new method utilizing Thermophilic Bacteria complex biological strengthening microbial inoculum to process high temperature oil extraction-generated waste water
CN105524889A (en) Preparation method of enzyme preparation for polycyclic aromatic hydrocarbon contaminated soil remediation
CN106119150B (en) A kind of dephosphorization microbial bacterial agent and its preparation method and application

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant