PSEUDOMONAS AERUGINOSA WITH MONOMETHYLAMINE DEGRADABILITY AND APPLICATION THEREOF

Abstract

The present invention discloses a strain of Pseudomonas aeruginosa with monomethylamine degradability and the application thereof. This strain, named Pseudomonas aeruginosa GDUTAN1, 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 2017283. This Pseudomonas aeruginosa GDUTAN1 was Gram-negative and rod-like, and round, green and opaque in the colony morphology, having a diameter of 1-2 mm. The Pseudomonas aeruginosa GDUTAN1 of the present invention can be applied to environmental remediation, degrading monomethylamine in the environment at a high degradation efficiency. When it degrades monomethylamine for 96 h at a substrate concentration of 50-140 mg/L, the degradation efficiency can reach more than 99%.

Claims

1. A strain of Pseudomonas aeruginosa with monomethylamine degradability, characterized in that: this strain, named Pseudomonas aeruginosa GDUTAN1, 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 2017283.

2. The Pseudomonas aeruginosa with monomethylamine degradability according to claim 1, characterized in that: the 16S rDNA sequence of the Pseudomonas aeruginosa GDUTAN1 is set forth in SEQ ID NO: 1.

3. Use of the Pseudomonas aeruginosa with monomethylamine degradability according to claim 1 in environmental remediation.

4. The use of the Pseudomonas aeruginosa with monomethylamine degradability in environmental remediation according to claim 3, characterized in that: the Pseudomonas aeruginosa GDUTAN1 is capable of degrading monomethylamine in the environment.

5. The use of the Pseudomonas aeruginosa with monomethylamine degradability in environmental remediation according to claim 3, characterized in that: the environment includes atmosphere, water or soil.

6. The use of the Pseudomonas aeruginosa with monomethylamine degradability in environmental remediation according to claim 4, characterized in that: the environment includes atmosphere, water or soil.

Description

BRIEF DESCRIPTION OF THE DRAWINGS

[0004] FIG. 1 shows the morphology of Pseudomonas aeruginosa GDUTAN1 of the present invention under an electron microscope.

DETAILED DESCRIPTION OF THE EMBODIMENTS

[0005] The present invention belongs to the field of microbial technology, and more particularly relates to a strain of Pseudomonas aeruginosa with monomethylamine degradability and the application thereof.

[0006] An object of the present invention is to overcome the deficiencies of the prior art and to provide a strain of Pseudomonas aeruginosa with monomethylamine degradability. Belonging to a new variant of Pseudomonas aeruginosa, the Pseudomonas aeruginosa GDUTAN1 has excellent monomethylamine degradability and can degrade monomethylamine in the environment at a high monomethylamine degradation efficiency.

[0007] Another object of the present invention is to provide an application of the above-described Pseudomonas aeruginosa with monomethylamine degradability in environmental remediation.

[0008] The objects of the present invention are achieved by the following technical solution:

[0009] The present invention, in a first aspect, provides a strain of Pseudomonas aeruginosa with monomethylamine degradability named Pseudomonas aeruginosa GDUTAN1, which 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 2017283.

[0010] The morphological characteristics of the Pseudomonas aeruginosa with monomethylamine degradability of the present invention are as follows:

[0011] (a) By using the physiological and biochemical identification methods of bacteria and electron microscopy, it was revealed that the Pseudomonas aeruginosa screened out was Gram-negative and rod-like with cell staining.

[0012] (b) Morphological characteristics of the colonies: After 24 h of culture in an LB solid medium, the colony appeared to be round, green and opaque, having a diameter of 1-2 meal.

[0013] The main physiological and biochemical characteristics of the Pseudomonas aeruginosa with monomethylamine degradability of the present invention are shown in Table 1 below:

TABLE-US-00001 TABLE 1 Main physiological and biochemical characteristics of Pseudomonas aeruginosa Items Test results Arabinose Xylose Glucose Mannitol Citrate utilization + DNA hydrolysis V-P test Nitrate (reduction) Siarch 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 +

[0014] The 16S rDNA sequence of the Pseudomonas aeruginosa with monomethylamine degradability of the present invention is set forth in SEQ ID NO: 1.

[0015] By alignment analysis of the 16S rDNA sequence, the strain of the present invention was found to have up to 100% homology with Pseudomonas aeruginosa DSM 5007. By combining the morphological characteristics, growth conditions, physiological and biochemical identification results of the bacteria, it was determined that Pseudomonas aeruginosa GDUTAN1 belongs to a new variant of Pseudomonas aeruginosa and was named Pseudomonas aeruginosa. GDUTAN1.

[0016] The present invention, in a second aspect, provides an application of the Pseudomonas aeruginosa with monomethylamine degradability in environmental remediation.

[0017] The Pseudomonas aeruginosa with monomethylamine degradability of the present invention is capable of degrading monomethylamine in the environment when used in environmental remediation.

[0018] Further, the environment includes the atmosphere, water or soil.

[0019] The use of the Pseudomonas aeruginosa GDUTAN1 of the present invention for the biodegradation of monomethylamine comprises the following preferred steps: Adjusting the pH of the substance containing monomethylamine to 5-9, and adding the enriched Pseudomonas aeruginosa GDUTAN1 bacterial solution in an inoculating amount of 0.5-2.5 mL, and then reacting at 20 C. to 40 C.;

[0020] the concentration of monomethylamine in the monomethylamine-containing substance is preferably 50-140 mg/L;

[0021] preferably, the reaction is carried out under oscillation conditions;

[0022] more preferably, the rate of oscillation is 100-250 rpm; and

[0023] preferably, the reaction time is 96-108 h.

[0024] Compared with the prior art, the present invention has the following beneficial effects:

[0025] 1. The strain of the present invention is Pseudomonas aeruginosa GDUTAN1 with monomethylamine degradability, which was obtained by screening the landfill leachate of a landfill in Guangzhou City, Guangdong Province for the first time.

[0026] 2. The Pseudomonas aeruginosa GDUTAN1 of the present invention has the ability to efficiently degrade monomethylamine; when it degraded monomethylamine for 96 h at a substrate concentration of 50-140 mg/L, the degradation efficiency could reach 99%.

[0027] The content of the present invention is further illustrated by the following specific examples, but these examples should not be construed as limiting the present invention. The technical means used in the examples are conventional means well known to those skilled in the art unless otherwise specified. Unless otherwise indicated, the reagents, methods, and devices employed in the present invention are routine in the art.

EXAMPLE 1

[0028] A strain of Pseudomonas aeruginosa with monomethylamine degradability, named Pseudomonas aeruginosa GDUTAN1, 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 2017283.

[0029] The Pseudomonas aeruginosa GDUTAN1 of the present example was isolated and screened from leachate of a landfill in Guangzhou City, Guangdong Province. The separation arid purification methods were as follows: The acclimation medium used was an inorganic salt medium (g/L) (each 1000 mL of the inorganic salt medium contains: K.sub.2HPO.sub.4.3H.sub.2O 1.2 g, KH.sub.2PO.sub.4 1.2 g, NH.sub.4Cl 0.4 g, MgSO.sub.4.7H.sub.2O 0.2 g, and FeSO.sub.4.7H.sub.2O 0.01 g; each 1 mL of the trace element solution contains: CaCl.sub.2.2H.sub.2O0.2 g, MnSO.sub.4.4H.sub.2O 0.2 g, CuSO.sub.4.2H.sub.2O 0.01 g, ZnSO.sub.4.7H.sub.2O 0.2 g, CoCl.sub.2.6H.sub.2O 0.09 g, Na.sub.2MoO.sub.4.2H.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. 1 mL of the enriched bacterial solution was taken and inoculated in a nutrient solution containing monomethylamine, 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. After acclimation, the acclimation solution was applied to a solid agar plate with monomethylamine as the sole carbon source (the solid medium containing monomethylamine was obtained by adding 18 g of agar and 4 mg of monomethylamine to per liter of the above inorganic salt medium), and cultured at 35 C. for 3 days; a single colony was selected and placed in a beef extract peptone medium (beef extract 3.0 g/L, peptone 10.0 g/L, NaCl 5.0 g/L, pH 7.4-7.6), and enriched and cultivated; the degradation efficiency of monomethylamine was determined, and the strain with the highest degradation efficiency was selected for purification.

[0030] Determination of degradation efficiency: Sampling periodically during the biodegradation of monomethylamine, and determining the degradation efficiency spectrophotometrically. Degradation efficiency=(initial concentrationfinal concentration)/initial concentration.

[0031] Spectrophotometric determination of monomethylamine concentration: Taking a certain amount of the monomethylamine degradation solution into a 10 mL colorimetric tube, diluting to 2.0 mL with an absorption solution (0.01 M HCl), and respectively adding 4.0 mL of 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), 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.

[0032] The purified colonies were identified, with the results as follows:

[0033] (1) Morphological characteristics of the bacteria:

[0034] a. By using the conventional physiological and biochemical identification methods of bacteria and electron microscopy, it was revealed that the Pseudomonas aeruginosa screened out was Gram-negative with cell staining; under the electron microscope, the bacterium was rod-like with a single flagellum, and had a size of (0.5 to 0.9)(0.5 to 1.5) m, as shown in FIG. 1;

[0035] b. morphological characteristics of the colonies: after 24 h of culture in an LB solid medium, the colony appeared to be neatly edged, round, green and opaque, having a diameter of 1-2 mm; and

[0036] c. the main physiological and biochemical characteristics of Pseudomonas aeruginosa are shown in Table 2:

TABLE-US-00002 TABLE 2 Physiological and biochemical characteristics of Pseudomonas aeruginosa 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 +

[0037] The above results indicate that the selected bacteria of the present invention had physiological and biochemical characteristics very similar to those of Pseudomonas aeruginosa.

[0038] (2) Extracting bacterial genomic DNA and using bacterial 16S rDNA universal primers:

TABLE-US-00003 Upstreamprimer:F27 (5-AGTTTGATCMTGGCTCAG-3) Downstreamprimer:R1492 (5-GGTTACCTTGTTACGACTT-3)

[0039] The entire 16S rDNA gene was amplified, with the sequencing results as shown in SEQ ID NO: 1.

[0040] By aligning the 16S rRNA gene sequence of 1331 by in length as shown in SEQ ID NO: 1 with the gene sequence registered in the Genbank, it was found that the strain had 100% homology with Pseudomonas aeruginosa DSM 5007.

[0041] Based on the above physiological and biochemical characteristics and 16S rRNA gene sequencing results, the selected strain of the present invention should belong to a new variant of Bacillus, and was named Pseudomonas aeruginosa GDUTAN1.

[0042] The Pseudomonas aeruginosa 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 2017283.

EXAMPLE 2

[0043] This example is the application of Pseudomonas aeruginosa GDUTAN1 in environmental remediation, which can degrade monomethylamine in the environment. The environment includes the atmosphere, water or soil.

[0044] The method for verifying the monomethylamine degradability of the selected Pseudomonas aeruginosa GDUTAN1 of the present invention is as follows:

[0045] Inoculating the Pseudomonas aeruginosa GDUTAN1 strain in the slant preservation into an LB enrichment culture solution, activating the bacteria at 35 C. for 24 h in a shaker at 150 rpm, and centrifuging the bacterial solution, and then collecting the bacteria. Resuspending with 5 mL of an inorganic salt solution (each 100 mL of the inorganic salt solution contains the following components: 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 inoculating 2.0 mL of the bacterial solution into 100 mL of an inorganic salt solution containing 50 mg/L of monomethylamine, with the pH of the inorganic salt at 6; reacting at 35 C. for 96 h in a shaker at 200 rpm, sampling periodically and determining the degradation efficiency spectrophotometrically. The degradation efficiency, measured in the same way as in Example 1, was determined to be 99.2%.

EXAMPLE 3

[0046] Inoculating the Pseudomonas aeruginosa GDUTAN1 strain in the slant preservation into an LB enrichment culture solution, activating the bacteria at 35 C. for 24 h in a shaker at 150 rpm, and centrifuging the bacterial solution, and then collecting the bacteria. Resuspending with 5 mL of an inorganic salt solution, and inoculating 2.0 mL, of the bacterial solution into 100 mL of an inorganic salt solution containing 50 mg/L of monomethylamine (the same as in Example 2), with the pH of the inorganic salt at 8; reacting at 35 C. for 96 h in a shaker at 100 rpm, sampling periodically and determining the degradation efficiency spectrophotometrically. The degradation efficiency, measured in the same way as in Example 1, was determined to be 41.5%.

EXAMPLE 4

[0047] Inoculating the Pseudomonas aeruginosa GDUTAN1 strain in the slant preservation into an LB enrichment culture solution, activating the bacteria at 35 C. for 24 h in a shaker at 150 rpm, and centrifuging the bacterial solution, and then collecting the bacteria. Resuspending with 5 mL of an inorganic salt solution, and inoculating 1.5 mL of the bacterial solution into 100 mL of an inorganic salt solution containing 80 mg/L of monomethylamine (the same as in Example 2), with the pH of the inorganic salt at 7; reacting at 20 C. for 96 h in a shaker at 150 rpm, sampling periodically and determining the degradation efficiency spectrophotometrically. The degradation efficiency, measured in the same way as in Example 1, was determined to be 98.9%.

EXAMPLE 5

[0048] Inoculating the Pseudomonas aeruginosa GDUTAN1 strain in the slant preservation into an LB enrichment culture solution, activating the bacteria at 35 C. for 24 h in a shaker at 150 rpm, and centrifuging the bacterial solution, and then collecting the bacteria. Resuspending with 5 mL of an inorganic salt solution, and inoculating 2.0 mL of the bacterial solution into 100 mL of an inorganic salt solution containing 110 mg/L of monomethylamine (the same as in Example 2), with the pH of the inorganic salt at 6; reacting at 25 C. for 96 h in a shaker at 200 rpm, sampling periodically and determining the degradation efficiency spectrophotometrically. The degradation efficiency, measured in the same way as in Example 1, was determined to be 99.9%.

EXAMPLE 6

[0049] Inoculating the Pseudomonas aeruginosa GDUTAN1 strain in the slant preservation into an LB enrichment culture solution, activating the bacteria at 35 C. for 24 h in a shaker at 150 rpm, and centrifuging the bacterial solution, and then collecting the bacteria. Resuspending with 5 mL of an inorganic salt solution, and inoculating 1.5 mL of the bacterial solution into 100 mL of an inorganic salt solution containing 140 mg/L of monomethylamine (the same as in Example 2), with the pH of the inorganic salt at 7; reacting at 30 C. for 96 h in a shaker at 150 rpm, sampling periodically and determining the degradation efficiency spectrophotometrically. The degradation efficiency, measured in the same way as in Example 1, was determined to be 99.0%.

[0050] 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.