<i>Lysinibacillus fusiformis </i>with methylamine degradability and application thereof

Abstract

The present invention discloses a strain of Lysinibacillus fusiformis with methylamine degradability and the application thereof. This strain, named Lysinibacillus fusiformis GDUTAN2, was deposited on May 24, 2017 in the China Center for Type Culture Collection in Wuhan University, Wuhan City, Hubei Province with a deposit number of CCTCC NO. M 2017284. This Lysinibacillus fusiformis GDUTAN2 was Grain-positive and rod-shaped, and the colony appeared to be round, white and transparent, having a diameter of 1-2 mm. The Lysinibacillus fusiformis GDUTAN2 of the present invention can be applied to environmental restoration, degrading methylamine in the environment at a high degradation efficiency. When it degraded methylamine for 96 h at a substrate concentration of 130 mg/L, the degradation efficiency could reach 32.8%.

Claims

1. A method for degrading methylamine, comprising: a) applying an effective amount of composition comprising Lysinibacillus fusiformis GDUTAN2 to a substrate containing methylamine, wherein the Lysinihaciiius fusiformis GDUTAN2 was deposited on May 24, 2017 in the China Center for Type Culture Collection in Wuhan University Wuhan City, Hubei Province with a deposit number of CCTCC NO. M 2017284; and b) contacting the substrate with the composition comprising L. fusiformis GDUTAN2 for a sufficient length of time to degrade the methylamine.

2. The method according to claim 1, wherein the 16S rDNA sequence of the Lysinibacillus fusiformis GDUTAN2 is set forth in SEQ ID NO:1.

3. The method according to claim 1, wherein the substrate includes atmosphere, water or soil.

4. The method according to claim 2, wherein the substrate includes atmosphere, water or soil.

Description

BRIEF DESCRIPTION OF THE DRAWINGS

(1) FIG. 1 shows the morphology of Lysinibacillus fusiformis GDUTAN2 of the present invention under an electron microscope.

DETAILED DESCRIPTION OF THE EMBODIMENTS

(2) The present invention will be further described with reference to the following specific examples, but these examples should not be construed as limiting the present invention. Unless otherwise specified, the technical means used in the examples are conventional means well known to those skilled in the art. Unless otherwise indicated, the reagents, methods, and devices employed in the present invention are routine in the art.

EXAMPLE 1

(3) A strain of Lysinibacillus fusiformis with methylamine degradability, named Lysinibacillus fusiformis GDUTAN2, was deposited on May 24, 2017 in the China Center for Type Culture Collection in Wuhan University (No. 299 Bayi Road, Wuchang District, Wuhan City, Hubei Province) with a deposit number of CCTCC NO. M 2017284.

(4) The Lysinibacillus fusiformis GDUTAN2 of the present example was isolated and screened from leachate of a landfill in Guangzhou City, Guangdong Province. The isolation and purification methods were as follows: The acclimation medium used was an inorganic salt medium (each 1000 mL of the inorganic salt medium contained K.sub.2HPO.sub.4.Math.3H.sub.2O 1.2 g, KH.sub.2PO.sub.4 1.2 g, NH.sub.4Cl 0.4 g, MgSO.sub.4.Math.7H.sub.2O 0.2 g, FeSO.sub.4.Math.7H.sub.2O 0.01 g, and 1 mL of a trace element solution, wherein the trace element solution contained CaCl.sub.2.Math.2H.sub.2O 0.2 g, MnSO.sub.4.Math.4H.sub.2O 0.2 g, CuSO.sub.4.Math.2H.sub.2O 0.01 g, ZnSO.sub.4.Math.7H.sub.2O 0.2 g, CoCl.sub.2.Math.6H.sub.2O 0.09 g, Na.sub.2MoO.sub.4.Math.2H.sub.2O 0.12 g, and H.sub.3BO.sub.3 0.006 g). First, 1 mL of the landfill leachate was taken and diluted 100 times, inoculated into a nutrient broth, and aerobically cultured at 37° C. for 1 day in a shaker at a rotational speed of 150 rpm. Then, 1 mL of the enriched bacterial solution was taken and inoculated in an inorganic salt nutrient solution containing methylamine, and aerobically cultured at 37° C. for 5 days in a shaker at a rotational speed of 150 rpm, and then moved to the next concentration in an inoculating amount of 10%, with the substrate acclimation gradients respectively at 10, 20, 50 and 100 mg/L. The final-concentration acclimation solution was diluted by 10.sup.−1 to 10.sup.−6, 200 μL of the dilutions diluted by 10.sup.−5 and 10.sup.−6 was respectively applied to a solid agar plate with methylamine as the sole carbon source (the solid medium containing methylamine was obtained by adding 18 g of agar and 4 mg of methylamine to per liter of the above inorganic salt medium), and the plate was placed into an incubator to culture at 35° C. for 3 days. A single colony of different morphology was selected for determination of the degradation efficiency of methylamine, and the strain with the highest degradation efficiency was selected for purification.

(5) Determination of degradation efficiency: Sampling periodically during the biodegradation of methylamine, and determining the degradation efficiency spectrophotometrically. Degradation efficiency=(initial concentration−final concentration)/initial concentration.

(6) Spectrophotometric determination of methylamine concentration: Taking a certain amount of methylamine degradation solution into a 10 mL colorimetric tube, diluting to 2.0 mL with an absorption solution (0.01 M HCl), and adding 4.0 mL of a buffer (obtained by dissolving 4.08 g of potassium dihydrogen phosphate and 1.6 g of borax in 80 mL of distilled water, adding 6.35 mL of 5.0 M NaOH solution, and diluting to 100 mL with water) and 0.4 mL of diazonium salt solution (obtained by adding 1.0 mL of sodium nitrite solution to 10 mL of p-nitrophenylamine hydrochloride solution and mixing), respectively, shaking well, letting stand for 40 min, adding 1.0 mL of 5 M NaOH solution, mixing, letting stand for 20 min, and performing colorimetric quantification at 510 nm.

(7) The purified colonies were identified, with the results as follows:

(8) (1) Morphological Characteristics of the Bacteria:

(9) a. By using the conventional physiological and biochemical identification methods of bacteria and electron microscopy, it was revealed that the Lysinibacillus fusiformis screened out was Grain-positive with cell staining; under the electron microscope, the bacterium was rod-shaped with flagella around, and had a size of (1.1 to 1.4) μm×(2.3 to 6.0) μm, as shown in FIG. 1;

(10) b. morphological characteristics of the colonies: after 24 h of culture in an LB solid medium, the colony appeared to be neatly edged, round, white and transparent, having a diameter of 1-2 mm; and

(11) c. the main physiological and biochemical characteristics of Lysinibacillus fusiformis are shown in Table 2.

(12) TABLE-US-00002 TABLE 2 Physiological and biochemical characteristics of Lysinibacillus fusiformis Items Test results Arabinose − Xylose − Glucose + Mannitol − Citrate utilization + DNA hydrolysis − V-P test − Nitrate (reduction) − Starch hydrolysis − Gelatin liquefaction + Anaerobic growth + 2% NaCl growth + 5% NaCl growth + pH = 5.5 growth + pH = 9.0 growth + Gram staining + 50° C. growth − 15° C. growth +

(13) The above results indicate that the selected bacteria of the present invention had physiological and biochemical characteristics very similar to those of the Lysinibacillus fusiform is genus.

(14) (2) Extracting Bacterial Genomic DNA and using Bacterial 16S rDNA Universal Primers:

(15) TABLE-US-00003 Upstream primer: F27 (5′-AGTTTGATCMTGGCTCAG-3′) Downstream primer: R1492 (5′-GGTTACCTTGTTACGACTT-3′)

(16) The entire 16S rDNA gene was amplified, with the sequencing results as shown in SEQ ID NO: 1.

(17) By aligning the 16S rRNA gene sequence of 1398 bp in length as shown in SEQ ID NO: 1 with the gene sequence registered in the Genbank, it was found that the homology between the strain and Lysinibacillus fusiformis KNUC423 was up to 100%.

(18) Based on the above physiological and biochemical characteristics and 16S rRNA gene sequence results, the strain of the present invention obtained by screening should belong to a new variant of the Bacillus genus, and was named Lysinibacillus fusiformis GDUTAN2.

(19) The Lysinibacillus fusiformis GDUTAN2 was deposited on May 24, 2017 in the China Center for Type Culture Collection (CCTCC) in Wuhan University (No. 299 Bayi Road, Wuchang District, Wuhan City, Hubei Province) with a deposit number of CCTCC NO. M 2017284.

EXAMPLE 2

(20) In this example, Lysinibacillus fusiformis GDUTAN2 was applied to environmental restoration, and could degrade methylamine in the environment. The environment includes atmosphere, water or soil.

(21) The methylamine degradability of the selected Lysinibacillus fusiformis GDUTAN2 of the present invention was tested as follows:

(22) The inorganic salt medium was prepared according to the needs of the degradation experiment: Adding 100 mL of an inorganic salt solution to a 300 mL serum bottle (per 100 mL of the inorganic salt solution contained K.sub.2HPO.sub.4.3H.sub.2O 0.12 g, KH.sub.2PO.sub.4 0.12 g, NH.sub.4Cl 0.04 g, MgSO.sub.4.7H.sub.2O 0.02 g, FeSO.sub.4.7H.sub.2O 0.001 g, CaCl.sub.2.2H.sub.2O 0.02 g, MnSO.sub.4.4H.sub.2O 0.02 g, CuSO.sub.4.2H.sub.2O 0.001 g, ZnSO.sub.4.7H.sub.2O 0.02 g, CoCl.sub.2.6H.sub.2O 0.009 g, Na.sub.2MoO.sub.4.2H.sub.2O 0.012 g, H.sub.3BO.sub.3 0.0006 g, and double distilled water 100 mL), and autoclaving at 121° C. for 30 min. First, activating the selected Lysinibacillus fusiformis GDUTAN2 with methylamine degradability in a nutrient broth medium (beef cream 3.0 g/L, peptone 10.0 g/L, and NaCl 5.0 g/L) at 30° C. for 24 h in a shaker at 100 rpm; and then, centrifuging the bacterial solution, collecting the bacteria, washing three times with a phosphate buffer, resuspending in 10 mL of an inorganic salt solution, and inoculating 1.0 mL of the bacterial solution into 100 mL of the inorganic salt solution containing different concentrations of methylamine; wherein the concentration of methylamine was 5, 10, 40, 70, 100 and 130 mg/L, respectively, the pH of the inorganic salt was 7, the reaction was carried out at 30° C. for 96 h in the shaker at 100 rpm, and sampling was made periodically to determine the degradation efficiency spectrophotometrically. The degradation efficiency was measured in the same way as in Example 1, and the results are shown in Table 3.

(23) TABLE-US-00004 TABLE 3 Degradation efficiencies of different initial concentrations of methylamine degraded by Lysinibacillus fusiformis GDUTAN2 Methylamine Degradation concentration (mg/L) rate   5 96.3%  10 88.1%  40 70.6%  70 52.2% 100 37.3% 130 32.8%

(24) As can be seen from Table 3, the Lysinibacillus fusiformis GDUTAN2 screened out by the present invention could degrade methylamine under this condition up to 96.3%.

(25) The above examples are preferred embodiments of the present invention, but the embodiments of the present invention are not limited thereto, and any other alterations, modifications, substitutions, combinations, and simplifications made without departing from the spirit and principle of the present invention should all be equivalent replacements and included in the scope of protection of the present invention.