CN105349464A - Pseudomonas cannabina MBC1 and application thereof - Google Patents
Pseudomonas cannabina MBC1 and application thereof Download PDFInfo
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- CN105349464A CN105349464A CN201510860778.4A CN201510860778A CN105349464A CN 105349464 A CN105349464 A CN 105349464A CN 201510860778 A CN201510860778 A CN 201510860778A CN 105349464 A CN105349464 A CN 105349464A
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- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
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- C12R2001/00—Microorganisms ; Processes using microorganisms
- C12R2001/01—Bacteria or Actinomycetales ; using bacteria or Actinomycetales
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- C12N1/00—Microorganisms, 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
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Abstract
The invention discloses pseudomonas cannabina MBC1. The preservation number of the pseudomonas cannabina MBC1 is CGMCC No.10817, the preservation date is May 19, 2015, and the preservation organization is the China General Microbiological Culture Collection Center. The strain can still survive and breed and has nitrogen fixation activity under the conditions of drought, large temperature difference, salt and alkali disasters and strong ultraviolet radiation. An inoculant prepared with the pseudomonas cannabina MBC1 can be applied to ecological systems characterized in drought, large temperature difference, salt and alkali disasters and strong ultraviolet radiation to increase nitrogen accumulation of the ecological systems, improve the soil environment, improve the biological activity of microorganisms and plants, and improve net primary productivity.
Description
Technical field
The invention belongs to biological nitrogen fixation field, be specifically related to a kind of azotobacter MBC1 and application thereof.
Background technology
Desert ecosystem accounts for 41% (Delgado-Baquerizo, etal., 2013) of global area, and its net primary productivity accounts for 20% (Whittaker, 1975) of terrestrial ecosystem productivity.In the middle of desert ecosystem, the scarcity of soil nitrogen nutrient seriously limits system net primary productivity (Asner, etal., 2003, Crutsinger, etal., 2013, Reich, etal., 2006).And desertification is also further developing, and result in land deterioration, nitrogen nutrient is running off serious.
Nitrogen input mode in physical environment is mainly biological nitrogen fixation.Nitrogen fixation increases soil can utilize nitrogen content, supplements nitrogen and promotes its metabolism and growth, to increase the primary productivity of the ecosystem, and also have vital effect for the Nitrogen Cycling of the ecosystem for microorganism and plant.Biological nitrogen fixation mainly contains symbiotic nitrogen fixation and from growing nitrogen-fixing.Due to Desert Area harsh environmental conditions, vegetation is rare, and the leguminous plants that therefore can carry out symbiotic nitrogen fixation is also very rare, is the main nitrogen input mode of desert ecosystem from growing nitrogen-fixing.Therefore, be of great importance from the recovery of growing nitrogen-fixing for desertification control work and desert ecosystem.
In order to help desertification control work, the investigation and application for desert soil azotobacter is extremely urgent.The current report for nitrogen-fixing bacteria is still based on symbiotic nitrogen-fixing bacteria, and the report for azotobacter is considerably less.And these azotobacter agent known on a small quantity all have requirement to the envrionment conditions such as envrionment temperature and humidity, resistance is poor, is applied in the middle of farmland or compost more, is unsuitable for the desert ecosystem of harsh environmental conditions.
Therefore be necessary to provide a kind of strong stress resistance, be applicable to the azotobacter strain with authigenic nitrogen fixation capacity of desert ecosystem.
Summary of the invention
The object of the present invention is to provide and be a kind ofly applicable to arid, large, the saline and alkaline disaster of the temperature difference and high uitraviolet intensity and can from the bacterial strain of growing nitrogen-fixing, to increase soil nitrogenase activity and available nitrogen content.
For reaching above object, the invention provides a kind of azotobacter (Pseudomonascannabina) MBC1, its preserving number is CGMCCNo.10817, and preservation date is on May 19th, 2015, and depositary institution is China Committee for Culture Collection of Microorganisms's common micro-organisms center.
Above-mentioned bacterial strains is Pseudomonascannabina.Strain Pseudomonas cannabina (bacterial classification name)-MBC1 (bacterial strain name), the topsoil sterile device of Desert Area is gathered cold condition taking back laboratory, through separation, pure culture, gramstaining, nitrogenase activity detect and 16srDNA order-checking gained.
Morphological character: this bacterial strain is observed and seen that cell is single, straight bacillus in gramstaining section, is not spirrillum.Size is generally 0.5-1 × 1.5-4 μm.Amphitrichous, does not produce sheath or prominence, does not have rest stage, do not form brood cell, without pod membrane, and Gram-negative.
Cultural characters: after this bacterial strain cultivates 3-7 days in 28 DEG C-30 DEG C on Ah Xu shellfish substratum, well-grown, obligate aerobic.Colonial morphology is different, most diameter 2-3mm, and edge is irregular, flat moistening.
Physiological property: decomposing protein ability is strong, but fermenting carbohydrate ability is lower, decomposition glucose, produces acid not aerogenesis, does not decompose N.F,USP MANNITOL, lactose and sugaring, can liquefy gelatin.Decomposing urea, does not form indoles, and magnesium oxide test is positive, can utilize citrate salt.
Functional performance: by inclined-plane Ah Xu shellfish culture medium culturing, measure with acetylene reduction method, this strains expressed has gone out nitrogenase activity.
Present invention also offers the microbial inoculum containing described azotobacter MBC1.Described microbial inoculum can be liquid bacterial agent, also can be solid fungicide.
Optionally, also containing thalline sorbing material in described microbial inoculum, described thalline sorbing material is selected from least one in the peat composed of rotten mosses, perlite, vermiculite power and micro mist calcium carbonate.
Optionally, in described microbial inoculum, the content of azotobacter MBC1 is 2.1 × 10
8-2.9 × 10
8cfu/g.
Preferably, in described microbial inoculum, the content of azotobacter MBC1 is 2.9 × 10
8cfu/g.
Optionally, the pH value of described microbial inoculum is 6.8-7.2.
Present invention also offers the preparation method of described microbial inoculum, comprise the following steps:
Described azotobacter MBC1 is inoculated in primary inclined plane substratum, cultivates 3-5 days at 28-30 DEG C, obtain one-level bacterial strain; By described one-level inoculation in secondary liquid substratum, under 28-30 DEG C of condition, 2-3 days is cultivated in concussion, obtains secondary bacterial strain; By described secondary inoculation in three grades of solid mediums, cultivate under 28-30 DEG C of condition and obtained three grades of bacterial strains after 1-2 days; By described three grades of bacterial strains and the peat composed of rotten mosses according to (2.1 × 10
8-2.9 × 10
8) cfu/g proportioning mixing even rear acquisition microbial inoculum, be preferably 2.9 × 10
8cfu/g;
Wherein, the formula of described primary inclined plane substratum is: KH
2pO
40.2g/L, MgSO
40.2g/L, NaCl0.2g, CaCO
35.0g, N.F,USP MANNITOL 10.0g, CaSO
40.1g, pH7.0, agar 20g, distilled water 1000mL;
The formula of secondary liquid substratum is: KH
2pO
40.2g/L, MgSO
40.2g/L, NaCl0.2g, CaCO
35.0g, N.F,USP MANNITOL 10.0g, CaSO
40.1g, pH7.0, distilled water 1000mL;
The formula of three grades of solid mediums is: N.F,USP MANNITOL 10.0g, yeast powder 1.0g, MgSO
47H
2o0.2g, K
2hPO
40.5g, NaCl0.1g, CaCl
20.05g, Rh liquid microelement 4.0mL, H
2o1000mL, agar 20g, pH6.8-7.0.
Present invention also offers described azotobacter MBC1 or the described application of azotobacter agent in soil improvement.
Optionally, described application comprise by described microbial inoculum and sand in mass ratio 1:9-11 be applied to soil surface after mixing.
Optionally, the consumption of described microbial inoculum is 420-560g microbial inoculum/mu.
Invention provides a kind of spontaneous nitrogen-fixing bacteria, and directly recording its nitrogenase activity by acetylene reduction method is 50.87nmol/ μ Lh.This bacterial strain extracts from the desert ecosystem environment of South of Maowusu Sandland.This area's drought; The whole year and day and night temperature large (Feng Wei, 2014); Soil alkaline disaster is serious, and strongly, especially summer, uitraviolet intensity was up to arriving 200-533 μ W/cm for ultraviolet
2(Pu Aiping, etal., 2005), radiation index is at about 8 grades.And generally in yield of radiation at 70-130 μ W/cm
2ultraviolet under, from 15s to 30min not etc., sterilizing rate can reach more than 99% (1988, Zhang Fuyun and conditions are all for Li Xiangyun, etal., 2006, Zhang Fengcai and Yuan and gloomy, 2005) to radiated time.The uitraviolet intensity in South of Maowusu Sandland summer is all starkly lower than when the uitraviolet intensity of common sterilising conditions and irradiation.This bacterial strain still can survival and reproduction have nitrogenase activity under arid, the large temperature difference, saline and alkaline disaster and strong ultraviolet radiation, especially this bacterium is not available for general bacterium to ultraviolet highly resistant, in today that Global climate change Ozone hole increase ultraviolet radiation is day by day strong, there is ecological significance and wide using value more.Its microbial inoculum made can be applied to the ecosystem of arid, high ultraviolet radiation, and can increase the nitrogen accumulation of these ecosystems, can play the effect of improvement edatope, improves the physiologically active of microorganism and plant, increases net primary productivity.Experiment shows, after this microbial inoculum being seeded in the naked husky surface 1 year of South of Maowusu Sandland without nitrogenase activity, its top layer can detect nitrogenase activity, is 461.78nmolC
2h
2m
-2h
-1, and available nitrogen too increases by 3.16mgkg
-1increase 22.1mgkg
-1.Briefly, the microbial inoculum that this bacterial strain is made has the advantages such as making is simple, low cost, drought-resistant, high UV light resistance and fixed nitrogen.
Preservation information: depositary institution is that China Committee for Culture Collection of Microorganisms's common micro-organisms center ChinaGeneralMicrobiologicalCultureCollectionCenter (is called for short CGMCC, address: No. 3, Yard 1, BeiChen xi Road, Chaoyang District, Beijing City, Institute of Microorganism, Academia Sinica, postcode 100101); Preservation date is on 05 19th, 2015; Register on the books and be numbered CGMCCNo.10817 in this preservation center; The Classification And Nomenclature of this preservation center suggestion is Pseudomonascannabina; Strain number is MBC1.
Embodiment
Following examples for illustration of the present invention, but are not used for limiting the scope of the invention.If do not specialize, the conventional means that in embodiment, technique means used is well known to those skilled in the art, is raw materials usedly commercial goods.
Embodiment 1
This bacterial strain extracts from the desert ecosystem top layer of South of Maowusu Sandland.This area's drought; The whole year and day and night temperature large (Feng Wei, 2014); Strongly, especially summer, uitraviolet intensity was up to arriving 200-533 μ W/cm for ultraviolet
2(Pu Aiping, etal., 2005), radiation index is at about 8 grades.And generally in yield of radiation at 70-130 μ W/cm
2ultraviolet under, from 15s to 30min not etc., sterilizing rate can reach more than 99% (1988, Zhang Fuyun and conditions are all for Li Xiangyun, etal., 2006, Zhang Fengcai and Yuan and gloomy, 2005) to radiated time.All be starkly lower than the uitraviolet intensity in South of Maowusu Sandland field in summer when the uitraviolet intensity of common sterilising conditions and irradiation, thus this bacterial strain has and has highly resistant to ultraviolet.
Take topsoil sample 10g and the sterilized water put into the 100mL of granulated glass sphere leaves standstill 20min, on rotary shaker, 200r/min fully vibrates 30min, soil supension.Draw the above-mentioned soil supension of 5.0mL respectively with Sterile pipette and add the aseptic dilution with water of 45mL, with Sterile pipette, bacteria suspension is added on solid Ah Xu shellfish substratum, cultivate under the condition of 28 DEG C.With plate streak purifying bacterial strain.The formula of Ah Xu the shellfish substratum that the present invention is used is: KH
2pO
40.2g/L, MgSO
40.2g/L, NaCl0.2g, CaCO
35.0g, N.F,USP MANNITOL 10.0g, CaSO
40.1g, pH7.0, agar 20g, distilled water 1000mL.
Bacterium will be screened and carry out Gram stain, and then under microscope (OLYMPUSBX51), observe ne ar and take pictures.
Then with liquid-transfering gun, the purifying bacterium colony 50 μ L in substratum is inoculated on inclined-plane Ah Xu shellfish solid medium, is placed on (30 DEG C) in incubator and cultivates three days, then measure nitrogenase activity with acetylene reduction method.Preliminary result shows the C adding 20%
2h
2time, the nitrogenase activity that sample shows is the highest, so C in this experiment
2h
2amount accounts for 20% of culture vessel volume.In order to enable experiment and from now on same experiments compare, sample is cultivated in illumination box ensure accurate envrionment conditions.In order to make result more close to actual value, the envrionment conditions in culture condition modeling effort district summer.Incubation time is 24h, and front 16h has illumination, and simultaneous temperature is 25 DEG C, and latter 8 hours unglazed photographs, simultaneous temperature is 15 DEG C.From Erlenmeyer flask, extract 50 μ L sample gas after cultivation, inject the gas chromatograph (Hitachi 163 type gas chromatograph) having walked steady baseline and measure ethylene emanation.With ethylene emanation (nmolC
2h
4/ m
-2h
-1) nitrogenase activity of this azotobacter strain is described, be 50.87nmol/ μ Lh.
Then identify showing the isolated bacterium with nitrogenase activity by the method for 16SrDNA recognition sequence, process is as follows: by phenol and chloroform extraction DNA of bacteria, dissolve, in 4 DEG C of preservations with Virahol.Then using 1.0 μ l (10pmol/ μ l) 27f and 1.0 μ l (10pmol/ μ l) 1496r as primer, 1.5 μ l DNA of bacteria are template, add 0.3 μ L (2.5mmol/Leach) dNTPs and 18.7 μ lddH
2o, is made into 25 μ l reaction systems.This is carried out PCR reaction, and 30 circulations, sex change, annealing and elongating temperature are 94 DEG C, 52 DEG C and 72 DEG C respectively, and this reaction completes on ABI-2720 instrument.PCR primer 1.5% agarose gel electrophoresis detects, and sample is in-20 DEG C of preservations.PCR primer is delivered to the order-checking of Hua Da genome company, by check order row and ncbi database the pattern bacterial sequences reported carry out similarity system design.
Embodiment 2
Azotobacter MBC1 is inoculated in primary inclined plane substratum, cultivates 4 days at 30 DEG C, obtain one-level bacterial strain; By one-level inoculation in secondary liquid substratum, under 30 DEG C of conditions, shake cultivation 3 days, obtain secondary bacterial strain; By secondary inoculation in three grades of solid mediums, cultivate under 30 DEG C of conditions and obtain three grades of bacterial strains after 2 days; Three grades of bacterial strains are contacted with the peat composed of rotten mosses after mixing and obtain microbial inoculum; The content of azotobacter MBC1 in microbial inoculum is made to be 2.9 × 10
8cfu/g, the pH value of microbial inoculum is 7.0.
Wherein, the formula of described primary inclined plane substratum is: KH
2pO
40.2g/L, MgSO
40.2g/L, NaCl0.2g, CaCO
35.0g, N.F,USP MANNITOL 10.0g, CaSO
40.1g, pH7.0, agar 20g, distilled water 1000mL;
The formula of secondary liquid substratum is: KH
2pO
40.2g/L, MgSO
40.2g/L, NaCl0.2g, CaCO
35.0g, N.F,USP MANNITOL 10.0g, CaSO
40.1g, pH7.0, distilled water 1000mL;
The formula of three grades of solid mediums is: N.F,USP MANNITOL 10.0g, yeast powder 1.0g, MgSO
47H
2o0.2g, K
2hPO
40.5g, NaCl0.1g, CaCl
20.05g, Rh liquid microelement 4.0mL, H
2o1000mL, agar 20g, pH6.8-7.0.
Described Rh liquid microelement: H
3bO
35.0g, Na
3moO
45.0g, H
2o1000mL.
Embodiment 3
Obtain mixture after the microbial inoculum of preparation in embodiment 2 and sand being mixed according to mass ratio 1:10, then this mixture is sprinkled upon South of Maowusu Sandland upper soll layer, the consumption of microbial inoculum is that consumption is about 500g microbial inoculum/mu.
After this microbial inoculum being seeded in the naked husky surface 1 year of South of Maowusu Sandland without nitrogenase activity, its top layer can detect nitrogenase activity, is 461.78nmolC
2h
2m
-2h
-1, and soil available nitrogen is also by 3.16mgkg
-1increase 22.1mgkg
-1.
Mu Us Shadi natural environmental condition is very severe, and major casualty weather has that arid, ultraviolet are excessively strong, strong wind, sandstorm, hot dry wind, frost, hail etc., is unfavorable for the existence of animals and plants and microorganism and breeds.Mu Us Shadi belongs to temperate continental climate in typical case, and its climate controlling factor is mainly northwest circulation, the especially long-time northern continent air mass controlled, and therefore day and night temperature is comparatively large, and temperature on average is lower, is about 6-7 DEG C; This area's drought, average precipitation is approximately 280mm, year potential evaporation amount be 2100-2500mm, frostless season is 128d, and absolute frostless season is 100d; Sandstorm is serious, and prevailing wind direction is northwest wind, and annual mean wind speed is about 2.8ms
-1, maximum wind speed can reach 15-18ms
-1, have more existing strong wind sky April November to next year then, Windy Days is 45.8d, can reach 52d at most, and annual sandstorm number of days is 20.6d; Soil alkaline degree is very high, and pH is 8.7-9.2 (Feng Wei, 2014); Strongly, especially summer, uitraviolet intensity was up to arriving 200-533 μ W/cm for ultraviolet
2(Pu Aiping, etal., 2005), radiation index is at about 8 grades.The discovery of this bacterial strain and the effect of inoculation of its microbial inoculum describe, dust storm, saline and alkaline disaster and intensive ultraviolet radiation large for arid, the temperature difference and have excellent tolerance, effectively can increase the nitrogen input capability of soil, add soil available nitrogen content.Especially, be 70-130 μ W/cm at ultraviolet radiation intensity
2time, from 15s to 30min not etc., sterilizing rate can reach more than 99% (1988, Zhang Fuyun and conditions are all for Li Xiangyun, etal., 2006, Zhang Fengcai and Yuan and gloomy, 2005) to radiated time usually.All be starkly lower than uitraviolet intensity and the time in South of Maowusu Sandland field in summer when the uitraviolet intensity of above-mentioned common sterilising conditions and irradiation, the general most bacteriums describing this bacterial strain and microbial inoculum ratio have special high UV light resistance.
Although above the present invention is described in detail with a general description of the specific embodiments, on basis of the present invention, can make some modifications or improvements it, this will be apparent to those skilled in the art.Therefore, these modifications or improvements without departing from theon the basis of the spirit of the present invention, all belong to the scope of protection of present invention.
Claims (10)
1. azotobacter (Pseudomonascannabina) MBC1, its preserving number is CGMCCNo.10817, and preservation date is on May 19th, 2015, and depositary institution is China Committee for Culture Collection of Microorganisms's common micro-organisms center.
2. the microbial inoculum containing azotobacter MBC1 described in claim 1.
3. microbial inoculum according to claim 2, is characterized in that, also containing thalline sorbing material in described microbial inoculum, described thalline sorbing material is selected from least one in the peat composed of rotten mosses, perlite, vermiculite power and micro mist calcium carbonate.
4. microbial inoculum according to claim 3, is characterized in that, described thalline sorbing material is the peat composed of rotten mosses.
5. microbial inoculum according to claim 4, is characterized in that, in described microbial inoculum, the content of azotobacter MBC1 is 2.1 × 10
8-2.9 × 10
8cfu/g, is preferably 2.9 × 10
8cfu/g.
6. according to the microbial inoculum in claim 2-5 described in any one, it is characterized in that, the pH value of described microbial inoculum is 6.8-7.2.
7. the preparation method of the microbial inoculum in claim 2-6 described in any one, is characterized in that, comprises the following steps:
Described azotobacter MBC1 is inoculated in primary inclined plane substratum, cultivates 3-5 days at 28-30 DEG C, obtain one-level bacterial strain; By described one-level inoculation in secondary liquid substratum, under 28-30 DEG C of condition, 2-3 days is cultivated in concussion, obtains secondary bacterial strain; By described secondary inoculation in three grades of solid mediums, cultivate under 28-30 DEG C of condition and obtained three grades of bacterial strains after 1-2 days; Be 2.1 × 10 by described three grades of bacterial strains and thalline sorbing material according to the content of azotobacter MBC1 in microbial inoculum
8-2.9 × 10
8microbial inoculum is obtained after the proportioning mixing of cfu/g;
Wherein, the formula of described primary inclined plane substratum is: KH
2pO
40.2g/L, MgSO
40.2g/L, NaCl0.2g, CaCO
35.0g, N.F,USP MANNITOL 10.0g, CaSO
40.1g, pH7.0, agar 20g, distilled water 1000mL;
The formula of secondary liquid substratum is: KH
2pO
40.2g/L, MgSO
40.2g/L, NaCl0.2g, CaCO
35.0g, N.F,USP MANNITOL 10.0g, CaSO
40.1g, pH7.0, distilled water 1000mL;
The formula of three grades of solid mediums is: N.F,USP MANNITOL 10.0g, yeast powder 1.0g, MgSO
47H
2o0.2g, K
2hPO
40.5g, NaCl0.1g, CaCl
20.05g, Rh liquid microelement 4.0mL, agar 20g, H
2o1000mL, pH6.8-7.0.
8. the application of azotobacter agent in soil improvement in azotobacter MBC1 or claim 2-6 according to claim 1 described in any one.
9. application according to claim 8, is characterized in that, comprise by described microbial inoculum and sand in mass ratio 1:9-11 be applied to soil surface after mixing.
10. application according to claim 8 or claim 9, it is characterized in that, the consumption of described microbial inoculum is 420-560g microbial inoculum/mu.
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| Publication number | Priority date | Publication date | Assignee | Title |
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| CN106754481A (en) * | 2016-11-26 | 2017-05-31 | 安徽省农业科学院园艺研究所 | The method and related culture medium of the azotobacter strain of resistance to high salt are screened from ice dish |
| CN106833674A (en) * | 2017-02-09 | 2017-06-13 | 东莞市环境科学研究所 | A kind of heavy-metal contaminated soil renovation agent preparation method |
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| CN201909721U (en) * | 2010-12-07 | 2011-07-27 | 北京林业大学 | Sampling and storing device for sand soil crust |
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Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106754481A (en) * | 2016-11-26 | 2017-05-31 | 安徽省农业科学院园艺研究所 | The method and related culture medium of the azotobacter strain of resistance to high salt are screened from ice dish |
| CN106754481B (en) * | 2016-11-26 | 2020-02-07 | 安徽省农业科学院园艺研究所 | Method for screening high-salt-resistant nitrogen-fixing strain from iceberg and related culture medium |
| CN106833674A (en) * | 2017-02-09 | 2017-06-13 | 东莞市环境科学研究所 | A kind of heavy-metal contaminated soil renovation agent preparation method |
| CN106833674B (en) * | 2017-02-09 | 2020-08-14 | 东莞市环境科学研究所 | Preparation method of heavy metal contaminated soil remediation agent |
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