CN110283743B - Degrading bacterium for degrading allelochemicals in plant root exudates and application thereof - Google Patents
Degrading bacterium for degrading allelochemicals in plant root exudates and application thereof Download PDFInfo
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Abstract
The invention relates to the field of microorganisms, and provides degrading bacteria for degrading allelochemicals in plant root exudates and application thereof, wherein the degrading bacteria are classified and named as Achromobacter xylosoxidans and Pseudomonas nitroreducens, and the preservation numbers of the strains are CGMCC NO.14517 and CGMCC NO.14518 respectively. The allelochemicals degrading bacteria can degrade various allelochemicals in plant root system secretion.
Description
Technical Field
The invention relates to the field of microorganisms, and provides a allelochemicals degrading bacterium for degrading allelochemicals in plant root exudates and application thereof.
Background
Peanuts are important oil and economic crops in China, and due to the limitation of soil utilization and relatively high economic benefits of the peanuts, the continuous cropping phenomenon of the peanuts is very common in the main peanut planting areas. However, continuous cropping of peanuts can generate the effect of continuous cropping obstacle, and the longer the continuous cropping period is, the more the yield and quality of peanuts are reduced, and the continuous development of peanut production is seriously influenced. The autotoxicity is one of the important reasons for the continuous cropping obstacle of peanuts. The autotoxicity is that root secretion and allelochemicals released by plant stubble inhibit the growth of plants. Allelochemicals secreted by root systems of peanuts, tobacco, cucumbers and the like all show inhibition effects on the plant height, the root length and the root system activity of plant seedlings, and the inhibition degree is enhanced along with the increase of the concentration of the allelochemicals. Previous studies found that peanut root secretive allelochemicals affect the microbial community structure of the root system, thereby causing the soil-borne diseases of the peanut to be aggravated.
At present, researches on allelochemicals degrading bacteria of peanuts are less. Benzoic acid and derivatives thereof are relatively important allelochemicals, and are detected in various plant root exudates, and early-stage research finds that benzoic acid has obvious inhibition on peanut germination and seedling growth.
Disclosure of Invention
In order to realize the purpose of the invention, the technical scheme adopted by the invention is as follows:
a degrading bacterium for degrading allelochemicals in plant root exudates is characterized in that the degrading bacterium is classified and named as Achromobacter xylosoxidans (Achromobacter xylosoxidans), is preserved in the common microorganism center of China Committee for culture Collection of microorganisms, and has the preservation date of 2017, 8 and 10 days, and the preservation number of the strain is CGMCC NO. 14517.
A degrading bacterium for degrading allelochemicals in plant root exudates is characterized in that the degrading bacterium is classified and named as nitroreduction Pseudomonas (Pseudomonas nitroreducens) and is preserved in the China general microbiological culture Collection center, the preservation date is 2017, 8 and 10 days, and the preservation number of the strain is CGMCC NO. 14518.
The invention also aims to provide the application of the degrading bacteria in degrading allelochemicals.
Another object of the present invention is to provide the use of the above-mentioned degrading bacteria for alleviating continuous cropping obstacles.
Further, the allelochemicals have benzene ring or long-chain saturated fatty acids.
Further, the allelochemicals are acetophenone, stearic acid, 3, 5-dimethylbenzaldehyde or palmitic acid.
Another object of the present invention is to provide a method for degrading allelochemicals, which is characterized by using Achromobacter xylosoxidans (Achromobacter xylosoxidans) of the present invention under the following degradation conditions: the pH value is 6.0-9.0, the temperature is 30-45 ℃, and the NaCl concentration is 0-6%.
Another object of the present invention is to provide a method for degrading allelochemicals, which is characterized by using Achromobacter xylosoxidans or Pseudomonas nitroreducens according to the present invention under the following degradation conditions: the pH value is 6.0-8.0, the temperature is 30-35 ℃, and the NaCl concentration is 0-4%.
Another object of the present invention is to provide a bacterial agent for degrading allelochemicals, which comprises the above degrading bacteria.
The adoption of the biodegradation technology is an effective measure for overcoming the self-toxicity of plants, has the advantages of repairing crops without influencing the growth of the crops, having no secondary pollution, being a high-efficiency and environment-friendly bioremediation method, and screening and separating allelochemicals and high-efficiency degrading bacteria which are key links of the technology. Two strains of high-efficiency allelochemicals degrading bacteria HJ-2 and HJ-3 are screened by an enrichment culture method and are identified as achromobacter xylosoxidans and Pseudomonas nitroreducens.
The application discovers that the achromobacter xylosoxidans HJ-2 and the pseudomonas nitroreducens HJ-3 can obviously degrade allelochemicals such as benzoic acid, acetophenone, 3, 5-dimethylbenzaldehyde and the like with benzene ring, stearic acid, palmitic acid and other long-chain saturated fatty acids, enriches the types of allelochemicals degrading bacteria, and provides reliable resource guarantee for relieving the autotoxicity of plants.
The degradation efficiency is a precondition for the application of the degrading bacteria. A plurality of autotoxic substance degrading bacteria are screened from apple rhizosphere by Qizhong and the like, and the degrading rate of the degrading bacteria BL2 with the best degrading efficiency to phthalic acid, p-hydroxybenzoic acid, phlorizin and pyrogallic acid is 66%, 72%, 84% and 84% respectively. The degradation rate of benzoic acid by 3 benzoic acid degrading bacteria isolated from Shigella sonchifolia et al is only 95.32%, 91.63% and 90.15%. The degradation rates of the separated degrading bacteria HJ-2 and HJ-3 to the benzoic acid respectively reach 96.88% and 92.65%, wherein the degrading bacteria HJ-2 has higher degradation efficiency compared with the researched degrading bacteria.
The degrading bacteria have practical application significance only by having stronger environment adaptability. This patent has analyzed the adaptation condition of two degradation fungus to environmental factors such as pH, temperature and NaCl concentration. pH has a great influence on the activity of cellular enzymes, and strong acid or strong base can cause protein denaturation and destroy cell membranes. 5 ginseng autotoxic substance degrading bacteria screened from Zhao Dongyue and the like are best in a growth state at pH 6.0-7.0, while degrading bacteria HJ-2 in the patent are suitable for pH 6.0-9.0, degrading bacteria HJ-3 are suitable for pH 6.0-8.0, 2 degrading bacteria have a better pH tolerance range, and the degrading bacteria HJ-2 have a wider pH tolerance range; too high or too low temperature can inhibit the activity of cellular enzyme, further influence the growth of microorganisms, and also can cause the reduction of the degradation efficiency of allelochemicals degrading bacteria. The suitable temperature of the degrading bacteria screened by Huangxingde and the like is lower than 40 ℃, the suitable temperature of the degrading bacteria HJ-2 in the research is 30-45 ℃, and the temperature range is wide; if the NaCl degree in the microbial growth environment is too high, the microbial osmotic pressure outside the cells is too high, and the cells die due to water shortage; in addition, excessive sodium ions can inhibit the activity of cellular enzymes, so that microorganisms have a certain NaCl concentration range, the degradation rate of the degrading bacteria HJ-2 is remarkably reduced after the NaCl concentration is increased to 6%, and the degradation rate of the degrading bacteria HJ-3 is remarkably reduced after the NaCl concentration is increased to 4%, which can be related to the inhibition of cells by NaCl. Screening achromobacter for degrading naphthalene by using cinnabar and the like, wherein the achromobacter can tolerate the concentration of 1-2% NaCl, and the degrading bacterium HJ-2 is also achromobacter in the patent, and the bacterium is suitable for the concentration of NaCl being 0-6%, can tolerate higher concentration of NaCl, and has better environment adaptability.
The peanut root system secretes a plurality of allelochemicals, the allelochemicals in the environment exist in a mixed form, and the screened degrading bacteria have practical application significance on whether the degrading bacteria can degrade other allelochemicals or not. Research shows that the Micrococcus liragmitis, the Chrysomyiame gaeulata and the Le & ltle & M.reuteri degrade main allelochemicals of the peanuts, such as oleic acid, hexadecanoic acid, phthalic acid and the like. The two degrading bacteria screened by the method can degrade various peanut allelochemicals, and particularly the degrading bacteria HJ-2 has stronger degrading capability, so that the degrading bacteria is an ideal strain for preventing and treating the autotoxicity of peanuts.
Compared with the prior art, the application has the following beneficial effects:
(1) 2 strains of high-efficiency allelochemicals degrading bacteria HJ-2 and HJ-3 are separated from healthy peanut rhizosphere soil in a continuous cropping peanut long-term positioning test base and are respectively identified as xylose-oxidizing Achromobacter (Achromobacter xylosoxidans HJ-2) and nitroreduction Pseudomonas (Pseudomonas nitroreducens HJ-3).
(2) The degradation characteristics of the degrading bacteria are measured through a single-factor test, the pH is 6.0-9.0, the suitable temperature is 30-45 ℃, and the suitable NaCl concentration is 0-6%; the degrading bacteria HJ-3 are suitable for degrading conditions with pH of 6.0-8.0, suitable temperature of 30-35 ℃ and suitable NaCl concentration of 0-4%.
(3) The two degrading bacteria can degrade various allelochemicals and have the characteristic of degrading the allelochemicals in a broad spectrum.
Drawings
FIG. 1 is a transmission electron microscope image of degrading bacteria HJ-2 and HJ-3;
FIG. 2 shows a phylogenetic tree constructed based on gene sequences of degrading bacteria HJ-2(A) and degrading bacteria HJ-3 (B);
FIG. 3 is a graph showing the effect of different pH, temperature and NaCl concentrations on the growth of the degrading bacteria HJ-2 and HJ-3.
Detailed Description
Sample source: digging 5 healthy plants from a peanut continuous cropping long-term positioning test field of a red soil ecological experimental station of Chinese academy of sciences in the flowering period of peanuts, removing large-particle soil blocks at roots, collecting rhizosphere soil by adopting a shaking method, respectively bagging, then bringing the rhizosphere soil back to a laboratory, and storing the rhizosphere soil at 4 ℃ for later use.
Seed medium (LB): 5g of beef extract, 10g of peptone and 5g of sodium chloride, and adding deionized water to a constant volume of 1L, wherein the pH value is 7.2-7.4;
inorganic salts Medium (MS): KH (Perkin Elmer)2PO43g，Na2HPO45g，NaCl 0.001g，CaCl2·H2O 0.003g，MgSO4·5H20.003g of O, and deionized water is added to the solution until the volume is 1L and the pH value is 7.0.
Selecting a culture medium: adding benzoic acid mother liquor (10 g. L) filtered by 0.22 μm microporous membrane into inorganic salt culture medium according to concentration requirement-1)。
The above solid culture medium is added with 2% agar, and sterilized at 121 deg.C for 20min under high pressure.
And (3) data analysis: plotting by using Excel 2016; data analysis was performed in SPSS 13.0 and significance analysis was performed in one way ANOVA.
Example 1
Screening degrading bacteria:
the screening of the degrading bacteria adopts an acclimation method which takes the benzoic acid as a unique carbon source and gradually increases the concentration of the benzoic acid. The specific operation is as follows: accurately weighing 10g of soil sample, adding the soil sample into a triangular flask filled with 90ml of sterile water, and fully shaking in a constant-temperature shaking table for 30min to prepare a mixture 1: a 10 concentration soil suspension. After the soil particles are precipitated, 1ml of supernatant is sucked and transferred into a test tube filled with 9ml of sterile water to prepare 10-2The bacterial suspension is prepared into 10 by the analogy-3、10-4、10-5、10-6、10-7The bacterial suspension of (4). Selection 10-4、10-5、10-6、10-7The four concentrations are respectively 100 μ L, and added into benzoic acid selection medium, wherein the concentration of benzoic acid is 5, 10, 15, 20 mg.L-1And sequentially improving gradient domestication and enriching degrading bacteria. Through multiple transfer culture, the culture solution is diluted in gradient and coated on 20 mg.L-1And (3) inversely culturing the mixture on a benzoic acid solid selection medium for 48 hours in a constant-temperature incubator at the temperature of 30 ℃. Selecting single colonies with different colony morphologies, inoculating the single colonies onto an LB solid culture medium, repeatedly streaking, separating and purifying to obtain pure strains, carrying out enrichment culture on the strains through a test tube inclined plane, and storing the strains in a refrigerator at 4 ℃ for later use.
The results of primary screening of degrading bacteria are shown in Table 1, and the results are 5, 10, 15 and 20 mg.L by taking benzoic acid as the only carbon source-1The concentration is sequentially increased, and gradient domestication and enrichment are carried out to screen out 6 degrading bacteria. Wherein the biomass of the degrading bacteria HJ-2 and HJ-3 is the largest, the OD values respectively reach 0.88 and 0.76, and the degradation rate of the benzoic acid reaches 96.88 percent and 92.65 percent.
TABLE 1 degradation rates of different strains of benzoic acid
Table 1 Degradation rate of Benzoic acid by different strains
Note that different letters in the same column indicate significant differences between treatments (P < 0.05). Notes The differences in a column indicator signature differences areas apparatus at P <0.05 levels.
Example 2
Identification of degrading bacteria:
(1) morphological characteristic identification of degrading bacteria
After the degrading bacteria are cultured for 18 hours in an LB culture medium, the shape, the size, the color, the transparency, the viscosity, the wettability, the swelling and edge characteristics of the degrading bacteria and whether pigment is produced or not are observed, and after the bacteria are dyed, the structures of gram stain, flagellum, capsule, spore and the like of the bacteria are observed by using a high-power microscope. After the bacterium liquid is dehydrated by glutaraldehyde-fixed ethanol and freeze-dried, the size and the surface structure of the thalli are observed by a scanning electron microscope.
(2) Determination of physiological and biochemical characteristics of degrading bacteria
Culturing degrading bacteria in LB culture medium for 18 hr, performing litmus milk, glucose, methyl red reaction, V-P test, indole reaction, citrate, starch hydrolysis, gelatin liquefaction, catalase, oxidase, oxygen demand, and H production according to literature2S and nitrate reduction and other physiological and biochemical tests.
The test result shows that: the degrading bacteria HJ-2 are yellow, convex, round and round in the outer edge, semitransparent, wet in surface, gram-negative and short rod-shaped (0.7-1.6 multiplied by 1.0-1.5 mu m) on the LB culture medium (figure 1), and the degrading bacteria HJ-3 are white, semitransparent, irregular in the edge, smooth in surface, gram-negative, rod-shaped (0.5-1 multiplied by 1.5-4 mu m) on the LB culture medium (figure 1); the degrading bacteria HJ-2 can react with glucose to produce acid without producing gas, can hydrolyze starch and liquefy gelatin, and is positive in catalase and aerobic, and the degrading bacteria HJ-3 catalase test, the oxidase test, the nitrate reduction test and the citrate test are positive (Table 2).
TABLE 2 morphological and physio-biochemical characteristics of degrading bacteria HJ-2 and HJ-3
Note that "+" is positive and "-" is negative
Note:“+”,Positive；“–”,Negative；
(3) Determination of degrading bacteria 16S rDNA gene sequence and construction of molecular phylogenetic tree
Degrading bacteria genome DNA total DNA of the strain is extracted by adopting a (quick extraction kit) kit, and a 16S rDNA universal primer 27F (forward primer) is used for: 5'-AGAGTTTGATCCTGGCTCAG-3', respectively; 1492R (reverse primer): 5'-TACGGGTACCTTGTTACGACTT-3', PCR amplification is carried out using the total DNA of the isolated degrading bacteria as a template. PCR reaction system (50. mu.L) 1. mu.L of DNA template, 5. mu.L of 10 XPCR Buffer, 4. mu.L of dNTP (2.5mmol/L), 1. mu.L of each primer (10. mu. mol/L), 0.5. mu.L of Tap enzyme (5U/. mu.L), and 37.5. mu.L of double distilled water. And (3) amplification procedure: 5min at 95 ℃, 45s at 94 ℃, 45s at 50 ℃ and 1min at 72 ℃ for 15 s; circulating for 32 times, and keeping the temperature at 72 ℃ for 10 min; after the reaction was completed, the size and specificity of the amplified fragment were examined by electrophoresis in 1% agarose. PCR products are detected and purified by agarose electrophoresis, sent to Shanghai workers for bidirectional sequencing and spliced output of a complete sequence, a 16S rDNA sequence is subjected to homology comparison with a 16S rDNA sequence recorded in Genebank, ClustalX 1.8 is adopted for sequence matching analysis, MEGA 6.0 software is used for constructing a phylogenetic tree by using an adjacency method (Neighbor-Joingmethod), and Bootstrap (1000 times of repetition) is used for checking the confidence of each branch.
Extracting genome DNA of the degrading bacteria, completing 16S rDNA gene sequencing, comparing the obtained sequence with known sequences in GenBank, and respectively constructing phylogenetic trees for two unknown degrading bacteria HJ-2 and HJ-3, wherein the result is shown in figure 2. According to 16S rDNA sequence homology comparison, the degrading bacteria HJ-2 and xylose oxidation Achromobacter (Achromobacter xylosoxidans) have recent homology and the sequence similarity is as high as 100 percent; HJ-3 has recent homology with Pseudomonas nitroreducens (Pseudomonas nitroreducens), and the sequence similarity reaches 99%. Combining the main morphological characteristics and physiological and biochemical characteristics of bacteria, sequencing results of degrading bacteria HJ-2 and HJ-3 are submitted to a GenBank database, and sequence accession numbers of MH324393 and MH324395 are obtained.
Example 3
Influence of environmental factors on degradation characteristics of degrading bacteria
In order to research the degradation conditions of the degrading bacteria HJ-2 and HJ-3 to the benzoic acid under different environmental conditions, 3 influencing factors of initial pH, temperature and NaCl concentration are selected as research objects to carry out single-factor experiments.
(1) Initial pH of culture
The degrading bacteria were inoculated at an inoculum size of 0.1% (OD600nm ═ 0.8) to a medium containing 20 mg. L-1Benzoic acid, inorganic salt culture solution with pH of 4, 5, 6, 7, 8, 9, 10, 30 deg.C, 180 r.min-1After shaking culture for 48h, the growth of thallus and the degradation rate of benzoic acid were determined, the growth of thallus was compared with that of non-inoculated degradation medium, and the treatment was repeated 3 times. The absorbance value at 600nm after treatment was determined, and the degradation rate of benzoic acid was the percentage of the difference in benzoic acid concentration before and after treatment to the initial benzoic acid concentration.
(2) Temperature of culture
The degrading bacteria were inoculated at pH 7.0 and 20 mg. L in an inoculum size of 0.1% (OD600nm ═ 0.8)-1In benzoic acid inorganic salt culture medium, the culture temperature is controlled at 25, 30, 35, 40, 45 ℃ and 180 r.min-1After shaking culture for 48h, the growth of thallus and the degradation rate of benzoic acid were determined, the growth of thallus was compared with that of non-inoculated degradation medium, and the treatment was repeated 3 times.
(3) Concentration of NaCl
The degrading bacteria were inoculated at pH 7.0 and 20 mg. L in an inoculum size of 0.1% (OD600nm ═ 0.8)-1In the benzoic acid inorganic salt culture medium, NaCl concentration is controlled to be 0, 2, 4, 6, 8, 10 mg/kg-1The culture temperature is 30 ℃, 180 r.min-1Shake culturing, and measuring thallus growth amount and benzoic acid degradation rate after 48h, wherein thallus growth amount is compared with culture medium without degrading bacteria, and the treatment is repeated for 3 times.
As shown in FIG. 3, the pH difference affects 2 degrading bacteria, the optimum pH value of the degrading bacteria HJ-2 is 6.0-9.0, the optimum pH value of the degrading bacteria HJ-3 is 6.0-8.0, and both the degrading bacteria are inhibited by too high or too low pH (FIG. 3A). As can be seen from FIG. 3B, the suitable growth temperature range of the degrading bacteria HJ-2 is wide, and the degrading bacteria HJ-2 can grow well at 30-45 ℃; the suitable growth temperature of the degrading bacteria HJ-3 is 30-35 ℃, and the degrading bacteria cannot tolerate high temperature. The degrading bacteria HJ-3 are sensitive to the change of NaCl degree (figure 3C), when the NaCl concentration is more than 4%, the growth of the degrading bacteria is inhibited, the optimum growth NaCl concentration is 0-4%, but the NaCl tolerance of the degrading bacteria HJ-2 is stronger, and the optimum NaCl concentration is 0-6%. In a word, the tolerance of the degrading bacteria HJ-2 to the adverse environment is stronger than that of the degrading bacteria HJ-3.
Example 4
Extracting the culture solution before and after treatment with 1: 1 mixture of ethyl alcohol and ethyl ether for 3 times, mixing the extractive solutions, rotary evaporating, methyl esterifying, cooling, extracting with N-hexane, and detecting the degradation rate with Gas Chromatograph (GC), wherein GC analysis is performed on Agilent gas chromatograph, and FID detector is used, GC condition is column model HP-FFAP, specification 30m × 0.32mm × 0.25.25 μm, no flow distribution, and carrier gas N is used2(99%) flow rate 14.0 ml. min-1Column temperature 220 ℃, temperature programming 10 ℃ for min-1And keeping the temperature at 220 ℃ for 10min, the temperature of a sample inlet is 260 ℃, the temperature of a detector is 260 ℃, and the sample injection amount is 1 mu l. Each treatment was repeated 3 times.
The degrading bacteria were inoculated into an inorganic salt medium (20 mg. L.) containing allelochemicals such as acetophenone, stearic acid, palmitic acid, lactic acid, 3, 5-dimethylbenzaldehyde and glycerol as the sole carbon source in an amount of 0.1% (OD600nm ═ 0.8)-1) The culture temperature is 30 ℃, 180 r.min-1After shaking culture for 48h, the thallus growth amount and allelochemicals degradation rate were determined, the thallus growth amount was compared with no degradation bacteria culture medium, and the treatment was repeated 3 times.
In order to investigate whether the screened degrading bacteria have degradation effects on other allelochemicals, degradation tests were performed using 6 peanut allelochemicals identified in the previous stage, such as acetophenone, stearic acid, 3, 5-dimethylbenzaldehyde, palmitic acid, lactic acid, and glycerol, and the results are shown in table 3. In inorganic salt taking allelochemicals as a unique carbon source, the degrading bacteria HJ-2 can effectively degrade 5 allelochemicals except that the growth of glycerol is poor; the degrading bacteria HJ-3 grow better by using stearic acid and palmitic acid as the only carbon source and grow the weakest in lactic acid and glycerol. Therefore, the two degrading bacteria can grow by using other allelochemicals as carbon sources, and have a broad-spectrum degrading function.
TABLE 3 degradation Properties of two degrading bacteria on different allelochemicals
Table 3 Degradation rate of strain HJ-2 and strain HJ-3
Claims (7)
1. A degrading bacterium for degrading allelochemicals in plant root exudates is characterized in that the degrading bacterium is classified and named as Achromobacter xylosoxidans (Achromobacter xylosoxidans), is preserved in the common microorganism center of China Committee for culture Collection of microorganisms, and has the preservation date of 2017, 8 and 10 days, and the preservation number of the strain is CGMCC NO. 14517.
2. Use of the degrading bacteria of claim 1 for degrading plant allelochemicals.
3. Use of the degrading bacteria of claim 1 for alleviating continuous cropping obstacles of peanuts.
4. Use according to claim 2, wherein the allelochemicals are acetophenone, stearic acid, 3, 5-dimethylbenzaldehyde or palmitic acid.
5. A method for degrading allelochemicals, comprising the use of the degrading bacteria of claim 1 under the conditions: the pH value is 6.0-9.0, the temperature is 30-45 ℃, and the NaCl concentration is 0-6%.
6. A method for degrading allelochemicals, comprising the use of the degrading bacteria of claim 1 under the conditions: the pH value is 6.0-8.0, the temperature is 30-35 ℃, and the NaCl concentration is 0-4%.
7. A bacterial agent for degrading allelochemicals, comprising the degrading bacterium according to claim 1.
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| CN110283743B (en) * | 2019-06-17 | 2020-10-09 | 扬州大学 | Degrading bacterium for degrading allelochemicals in plant root exudates and application thereof |
| CN111480531A (en) * | 2020-05-26 | 2020-08-04 | 湖南省蔬菜研究所 | Method for relieving continuous cropping obstacle of watermelons |
| CN116240156A (en) * | 2022-12-31 | 2023-06-09 | 广西中医药大学 | Screening method for reducing pseudo-ginseng autotoxic substance microbial strains |
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| CN101914466B (en) * | 2010-07-02 | 2011-12-07 | 郑州大学 | Achromobacter xylosoxidans and application thereof for degrading o-aminobenzoic acid |
| US9150840B2 (en) * | 2011-08-26 | 2015-10-06 | Council Of Scientific & Industrial Research | Isolated bacterial strain of Achromobacter sp. MTCC 5605 and a highly enantioselective epoxide hydrolase isolated therefrom |
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