CN109517770B - Aerobic facultative autotrophic denitrifying bacterium and application thereof - Google Patents

Aerobic facultative autotrophic denitrifying bacterium and application thereof Download PDF

Info

Publication number
CN109517770B
CN109517770B CN201910073844.1A CN201910073844A CN109517770B CN 109517770 B CN109517770 B CN 109517770B CN 201910073844 A CN201910073844 A CN 201910073844A CN 109517770 B CN109517770 B CN 109517770B
Authority
CN
China
Prior art keywords
autotrophic denitrifying
denitrifying bacterium
pseudomonas
aerobic facultative
aerobic
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
CN201910073844.1A
Other languages
Chinese (zh)
Other versions
CN109517770A (en
Inventor
张多英
张彦龙
白也
雷虹
曾伟民
赵丹丹
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.)
Heilongjiang University
Original Assignee
Heilongjiang 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 Heilongjiang University filed Critical Heilongjiang University
Priority to CN201910073844.1A priority Critical patent/CN109517770B/en
Publication of CN109517770A publication Critical patent/CN109517770A/en
Application granted granted Critical
Publication of CN109517770B publication Critical patent/CN109517770B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

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
    • C12N1/205Bacterial isolates
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12RINDEXING SCHEME ASSOCIATED WITH SUBCLASSES C12C - C12Q, RELATING TO MICROORGANISMS
    • C12R2001/00Microorganisms ; Processes using microorganisms
    • C12R2001/01Bacteria or Actinomycetales ; using bacteria or Actinomycetales
    • C12R2001/38Pseudomonas
    • 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
    • C02F3/02Aerobic processes
    • 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
    • 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
    • C12N1/02Separating microorganisms from their culture media
    • 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
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • C02F2101/163Nitrates
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

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

Abstract

The invention discloses an aerobic facultative autotrophic denitrifying bacterium and application thereof, and relates to the aerobic facultative autotrophic denitrifying bacterium and application thereof. The aerobic facultative autotrophic denitrifying bacterium is Pseudomonas (Pseudomonas koreensis) Y5-11, is preserved in the common microorganism center of China Committee for culture Collection of microorganisms, has the preservation address of No. 3 Xilu No.1 Beijing, Chaoyang district, the preservation date of 2018, 10 months and 29 days, and the preservation number of 16651. The strain of the invention can not only utilize organic carbon source for growth, but also can use CO for growth2The invention is used for reducing nitrate by a unique carbon source and is applied to the technical field of environmental microorganisms.

Description

Aerobic facultative autotrophic denitrifying bacterium and application thereof
Technical Field
The invention relates to an aerobic facultative autotrophic denitrifying bacterium and application thereof.
Background
Denitrification by microorganisms refers to the process by which microorganisms reduce nitrate to nitrogen. This phenomenon is common in nature (land, fresh water and marine systems). Denitrification is generally considered to be divided into anoxic-heterotrophic denitrification and anaerobic-autotrophic denitrification. The anoxic-heterotrophic denitrification is a process of reducing nitrate to nitrogen under an anoxic condition (dissolved oxygen is about 0.5 mg/L) by using organic matters (organic carbon) as electron donors. The characteristic of anoxic-heterotrophic denitrification is that a large amount of organic carbon source is required to sustain growth (C/N)>10) In the denitrification treatment process of sewage or slightly polluted underground water, the condition of insufficient carbon source often occurs, and organic matters such as methanol and the like are generally required to be additionally added, so that the water production cost is increased. The anaerobic-autotrophic denitrifying bacteria do not need organic carbon source and use CO2、HCO3 -Or CO3 2-The bacteria can be divided into hydrogen autotrophic denitrifying bacteria and sulfur autotrophic denitrifying bacteria according to different electron donors. Since the anaerobic-autotrophic denitrifying bacteria are obligate anaerobes and require additional supply of electron donors (i.e., hydrogen or sulfide), these characteristics increase the difficulty and cost of application of the anaerobic-autotrophic denitrifying bacteria. In recent years, a great deal of research and discovery shows that heterotrophic nitrification-aerobic denitrification bacteria exist, so that denitrification reaction can be carried out under aerobic conditions, however, the bacteria still need high organic carbon sources (usually, the C/N is 10-20).
Disclosure of Invention
The invention provides an aerobic facultative autotrophic denitrifying bacterium and application thereof.
The aerobic facultative autotrophic denitrifying bacterium is Pseudomonas koreensis Y5-11, is preserved in the common microorganism center of China Committee for culture Collection of microorganisms, has the preservation address of No. 3 Xilu No.1 Beijing, Chaoyang district, the preservation date of 2018, 10 and 29 days, and the preservation number of 16651.
The aerobic facultative autotrophic denitrifying bacterium is applied to removing pollutants in underground water.
The screening method of the aerobic facultative autotrophic denitrifying bacteria Y5-11 comprises the following steps: putting 100mL of low-temperature (about 4 ℃) underground water sample into a 4 ℃ incubator for enrichment culture, and periodically adding 0.1g/L NaNO3(ii) a After 7-10 days, the water sample is obviously turbid, the growth of microorganisms is indicated, and the water sample is transferred into a separation and purification solid culture medium; the separation and purification temperature is 6-10 ℃, the culture time of the separation and purification is 3-4 d, after 3 times of purification, the thalli staining observation is carried out, and when no mixed bacteria exist in bacterial colonies, the bacterial colonies are pure bacterial strains and are used for carrying out screening test; and carrying out liquid culture on the separated and purified strains, collecting thalli, inoculating the thalli into a 100mg/L nitrate solution, measuring the concentration of the residual nitrate and calculating the denitrification rate after 30min under the conditions of 6-10 ℃ and the rotating speed of a shaking table of 180rpm/min, and selecting the strains capable of carrying out denitrification, namely the aerobic facultative autotrophic denitrifying bacteria.
Extracting genome DNA of the aerobic facultative autotrophic denitrifying bacteria, performing 16S rDNA sequence amplification, using the obtained fragments for sequencing, identifying the fragments into Pseudomonas koreensis according to gene characteristics of the aerobic facultative autotrophic denitrifying bacteria and Bergey bacteria identification handbook, and finally naming the fragments as Pseudomonas koreensis Y5-11.
The Pseudomonas koreensis Y5-11 of the invention can not only utilize organic carbon source for growth, but also CO2Nitrate is reduced for the sole carbon source and no additional electron donor is required. The nitrification rate of Y5-11 under the condition of no carbon source is measured, and when the nitrate concentration reaches 150.0mg/L, the denitrification rate is the highest and is 135.12 mg/L/h.
The Pseudomonas koreensis Y5-11 is preserved in the common microorganism center of China Committee for culture Collection of microorganisms, the preservation address is No. 3 of West Lu No.1 Hospital, Chaojing, Chaoyang, the preservation date is 2018, 10 months and 29 days, and the preservation number is 16651.
Drawings
FIG. 1 is a schematic diagram showing the gram stain result of aerobic facultative autotrophic denitrifying bacteria Y5-11 according to the present invention;
FIG. 2 is a schematic diagram showing the colony of aerobic facultative autotrophic denitrifying bacterium Y5-11 according to the present invention.
Detailed Description
The first embodiment is as follows: the aerobic facultative autotrophic denitrifying bacterium is Pseudomonas koreensis Y5-11, is preserved in the common microorganism center of China Committee for culture Collection of microorganisms, has the preservation address of No. 3 Hosieboldo No.1 of Beijing Kogyo Chen, the preservation date of 2018, 10 and 29 days, and the preservation number of 16651.
The screening method of the aerobic facultative autotrophic denitrifying bacterium Pseudomonas koreensis Y5-11 in the embodiment comprises the following steps: putting 100mL of low-temperature (about 4 ℃) underground water sample into a 4 ℃ incubator for enrichment culture, and periodically adding 0.1g/L NaNO3(ii) a After 7-10 days, the water sample is obviously turbid, the growth of microorganisms is indicated, and the water sample is transferred into a separation and purification solid culture medium; the main components of the culture medium are as follows: NaNO3 0.1~0.5g/L,MnSO4 0.01~0.05g/L,(NH4)2Fe(SO4)2·6H2O 0.01~0.10g/L,CaCl2 0.01~0.05g/L,Na2HPO4 0.3~0.9g/L,MgSO4·7H20.01-0.05 g/L of O, 0.3-0.9 g/L of NaCl and 7.0-7.4 of pH value, (1.8 g/L of agar is added into a solid culture medium); the separation and purification temperature is 6-10 ℃, the culture time of the separation and purification is 3-4 d, after 3 times of purification, the thalli staining observation is carried out, and when no mixed bacteria exist in bacterial colonies, the bacterial colonies are pure bacterial strains and are used for carrying out screening test; and carrying out liquid culture on the separated and purified strains, collecting thalli, inoculating the thalli into a 100mg/L nitrate solution, measuring the concentration of the residual nitrate and calculating the denitrification rate after 30min under the conditions of 6-10 ℃ and the rotating speed of a shaking table of 180rpm/min, and selecting the strains capable of carrying out denitrification, namely the aerobic facultative autotrophic denitrifying bacteria.
Extracting genome DNA of the aerobic facultative autotrophic denitrifying bacteria, performing 16S rDNA sequence amplification, using the obtained fragments for sequencing, identifying the fragments into Pseudomonas koreensis according to gene characteristics of the aerobic facultative autotrophic denitrifying bacteria and Bergey bacteria identification handbook, and finally naming the fragments as Pseudomonas koreensis Y5-11.
The Pseudomonas koreensis Y5-11 of the invention can not only utilize organic carbon source for growth, but also CO2Nitrate is reduced for the sole carbon source and no additional electron donor is required. The denitrification rate of Y5-11 was determined, and when the nitrate concentration reached 150.0mg/L, the denitrification rate was the highest, 135.12 mg/L/h.
The second embodiment is as follows: the first difference between the present embodiment and the specific embodiment is: the aerobic facultative autotrophic denitrifying bacterium Pseudomonas koreensis Y5-11 is gram-negative, bacillus, 2-4 mu m in length and 0.5-0.9 mu m in width, has no spores and flagella, moves by virtue of the flagella, has capsules, forms milky colonies on an LB culture medium, and is irregular and circular, and the surface of the colonies is convex. The rest is the same as the first embodiment.
The third concrete implementation mode: the aerobic facultative autotrophic denitrifying bacteria are applied to removing pollutants in underground water.
The fourth concrete implementation mode: the third difference between the present embodiment and the specific embodiment is that: the contaminant is nitrate. The rest is the same as the third embodiment.
The fifth concrete implementation mode: the screening method of the aerobic facultative autotrophic denitrifying bacterium Pseudomonas koreensis Y5-11 in the embodiment comprises the following steps: putting 100mL of low-temperature (about 4 ℃) underground water sample into a 4 ℃ incubator for enrichment culture, and periodically adding 0.1g/L NaNO3(ii) a After 7-10 days, the water sample is obviously turbid, the growth of microorganisms is indicated, and the water sample is transferred into a separation and purification solid culture medium; the main components of the culture medium are as follows: NaNO3 0.1~0.5g/L,MnSO40.01~0.05g/L,(NH4)2Fe(SO4)2·6H2O 0.01~0.10g/L,CaCl2 0.01~0.05g/L,Na2HPO4 0.3~0.9g/L,MgSO4·7H20.01-0.05 g/L of O, 0.3-0.9 g/L of NaCl and 7.0-7.4 of pH value, (1.8 g/L of agar is added into a solid culture medium); the temperature for separation and purification is 6-10 ℃, and the culture time for separation and purification is3-4 d, after 3 times of purification, carrying out thallus staining observation, and when no mixed bacteria exist in the bacterial colony, obtaining a pure bacterial strain for carrying out a screening test; and carrying out liquid culture on the separated and purified strains, collecting thalli, inoculating the thalli into a 100mg/L nitrate solution, measuring the concentration of the residual nitrate and calculating the denitrification rate after 30min under the conditions of 6-10 ℃ and the rotating speed of a shaking table of 180rpm/min, and selecting the strains capable of carrying out denitrification, namely the aerobic facultative autotrophic denitrifying bacteria.
The aerobic facultative autotrophic denitrifying bacterium Pseudomonas koreensis Y5-11 is gram-negative, bacillus, 2-4 mu m in length and 0.5-0.9 mu m in width, has no spores and flagella, moves by virtue of the flagella, has capsules, forms milky colonies on an LB culture medium, and is irregular and circular, and the surface of the colonies is convex. The gram stain results for Y5-11 are shown in FIG. 1; the colonies of Y5-11 are shown in FIG. 2.
A reference method for measuring the physiological and biochemical characteristics of aerobic facultative autotrophic denitrifying bacteria Pseudomonas koreensis Y5-11 (Dongxu bead, Chuia Miaoying. general bacteria system identification manual. Beijing: scientific Press, 2001.) is provided. The physiological and biochemical characteristics of the aerobic facultative autotrophic denitrifying bacteria in the embodiment are as follows: catalase and oxidase are positive, Tween 80 and arginine can be hydrolyzed, gelatin liquefaction can be carried out, and nitrate can be reduced to generate nitrogen; the glucose can not be hydrolyzed to produce acid, and the starch can not be hydrolyzed; d-arabitol, D-fructose, D-galactose, alpha-D-glucose, D-mannitol, methylpropionic acid, methylsuccinic acid, acetate, propionate, butyrate, citrate, ethanol, benzoate, malate, and lactate may be utilized. : catalase and oxidase are positive, Tween 80 and arginine can be hydrolyzed, gelatin liquefaction can be carried out, and nitrate can be reduced to generate nitrogen; the glucose can not be hydrolyzed to produce acid, and the starch can not be hydrolyzed; d-arabitol, D-fructose, D-galactose, alpha-D-glucose, D-mannitol, methylpropionic acid, methylsuccinic acid, acetate, propionate, butyrate, citrate, ethanol, benzoate, malate, and lactate may be utilized.
The sixth specific implementation mode: identification of Pseudomonas koreensis Y5-11 of the present embodiment:
extracting genome DNA of aerobic facultative autotrophic denitrifying bacterium Pseudomonas koreensis Y5-11, and then carrying out 16S rDNA sequence amplification: the PCR primers used for amplification are universal primers: a forward primer 5'-CAGAGTTTGATCCTGGCT-3'; the reverse primer 5'-AGGAGGTGATCCAGCCGCA-3'. The PCR reaction system is as follows: 20-50 ng template DNA, 0.2. mu.L Taq enzyme, 2.5. mu.L 10 XBuffer (containing Mg2+), 1. mu.L dNTP (2.5 mmol/L each), 0.5. mu.L forward primer, 0.5. mu.L reverse primer, and sterile deionized water was added to 25. mu.L. PCR amplification conditions: pre-denaturation at 94 ℃ for 4min, denaturation at 94 ℃ for 45s, amplification at 55 ℃ for 45s, extension at 72 ℃ for 1min, 30 cycles, extension at 72 ℃ for 10min, and termination of reaction at 4 ℃, wherein the obtained fragment is used for sequencing, and the gene sequence is shown as SEQ ID NO: 1, GenBank registration number is MH 817853. According to the gene characteristics of aerobic facultative autotrophic denitrifying bacteria and Bergey's Manual of identification of bacteria, the strain is identified as Pseudomonas koreensis of the genus Pseudomonas, and finally named as Pseudomonas koreensis Y5-11.
The denitrification function of the Pseudomonas koreensis Y5-11 of the embodiment is verified under the conditions of low temperature and no addition of organic carbon source:
test 1: measuring the denitrification rate of aerobic facultative autotrophic denitrifying bacterium Pseudomonas koreensis Y5-11 at 6-10 ℃ under the condition of no organic carbon source: simulating the water quality of underground water: respectively preparing nitrate solutions with the concentrations of 10.0, 20.0, 40.0, 60.0, 100.0, 150.0 and 200.0mg/L, and then adding MnSO4And FeSO4Mixed solution of MnSO4The concentration is 7-10 mg/L, FeSO4The concentration is 5-8 mg/L; the strain Pseudomonas koreensis Y5-11 was then cultured to 10%7~109And (2) centrifuging 50mL of bacterial liquid at 6000g for 10min to obtain thallus precipitates, cleaning the thallus precipitates for 2-3 times by using sterile deionized water, transferring the thallus into 50mL of simulated underground water, measuring the concentration of the residual nitrate after 30min, and calculating the denitrification rate, wherein when the concentration of the nitrate reaches 150.0mg/L, the denitrification rate is the highest and is 135.12 mg/L/h. When the nitrate concentration exceeds 150mg/L, the denitrification rate tends to decrease.
As can be seen from the tests, Pseudomonas koreensis Y5-11 can be expressed as CO2The nitrate is reduced by the single carbon source without additionally providing an electron donor, and the denitrification rate is 135.12mg/L/h under the conditions of 6-10 ℃ and no carbon source and when the concentration of the nitrate reaches 150.0 mg/L.
Test 2: 50mL of 4 samples of actual groundwater were collected from different groundwater samples, and the water quality was as shown in Table 1.
TABLE 1 groundwater quality
Figure BDA0001958118520000051
Is to culture the strain Pseudomonas koreensis Y5-11 to 107~109And (2) centrifuging 50mL of bacterial liquid at 6000g for 10min to obtain thallus precipitates, cleaning the thallus precipitates for 2-3 times by using sterile deionized water, collecting the thallus, transferring the thallus into 4 water samples respectively, determining the concentration of the residual nitrate in the water after treating for 30min and 8h, and calculating the removal rate of the nitrate, wherein the results are shown in Table 2. The result shows that Y5-11 can remove about 80% of nitrate in the groundwater after 8h treatment, and the nitrate can meet the requirements of sanitary Standard for Drinking Water (GB5749-2006) in China (when groundwater is used as water source, the nitrate is less than or equal to 20mg/L)
TABLE 2Pseudomonas koreensis Y5-11 effect on nitrate removal from groundwater after 30min and 8h
Figure BDA0001958118520000052
As can be seen from tests 1 and 2, Pseudomonas koreensis Y5-11 can be expressed as CO2The nitrate is reduced by the single carbon source without additionally providing an electron donor, and the denitrification rate is 135.12mg/L/h under the conditions of 6-10 ℃ and no carbon source and when the concentration of the nitrate reaches 150.0 mg/L. Y5-11 can remove about 80% of nitrate in groundwater after 8h of treatment without adding extra carbon source and electron donor.
Sequence listing
<110> university of Heilongjiang
<120> aerobic facultative autotrophic denitrifying bacterium and application thereof
<160> 3
<210> 1
<211> 1405
<212> DNA
<213> Pseudomonas (Pseudomonas koreensis)
<400> 1
gcagtcgagc ggatgagagg agcttgctcc tggattcagc ggcggacggg tgagtaatgc 60
ctaggaatct gcctggtagt gggggacaac gtttcgaaag gaacgctaat accgcatacg 120
tcctacggga gaaagcaggg gaccttcggg ccttgcgcta tcagatgagc ctaggtcgga 180
ttagctagtt ggtgaggtaa tggctcacca aggcgacgat ccgtaactgg tctgagagga 240
tgatcagtca cactggaact gagacacggt ccagactcct acgggaggca gcagtgggga 300
atattggaca atgggcgaaa gcctgatcca gccatgccgc gtgtgtgaag aaggtcttcg 360
gattgtaaag cactttaagt tgggaggaag ggttgtagat taatactctg caattttgac 420
gttaccgaca gaataagcac cggctaactc tgtgccagca gccgcggtaa tacagagggt 480
gcaagcgtta atcggaatta ctgggcgtaa agcgcgcgta ggtggtttgt taagttggat 540
gtgaaatccc cgggctcaac ctgggaactg catccaaaac tggcaagcta gagtatggta 600
gagggtggtg gaatttcctg tgtagcggtg aaatgcgtag atataggaag gaacaccagt 660
ggcgaaggcg accacctgga ctgatactga cactgaggtg cgaaagcgtg gggagcaaac 720
aggattagat accctggtag tccacgccgt aaacgatgtc aactagccgt tgggagcctt 780
gagctcttag tggcgcagct aacgcattaa gttgaccgcc tggggagtac ggccgcaagg 840
ttaaaactca aatgaattga cgggggcccg cacaagcggt ggagcatgtg gtttaattcg 900
aagcaacgcg aagaacctta ccaggccttg acatccaatg aactttccag agatggattg 960
gtgccttcgg gagcattgag acaggtgctg catggctgtc gtcagctcgt gtcgtgagat 1020
gttgggttaa gtcccgtaac gagcgcaacc cttgtcctta gttaccagca cgttatggtg 1080
ggcactctaa ggagactgcc ggtgacaaac cggaggaagg tggggatgac gtcaagtcat 1140
catggccctt acggcctggg ctacacacgt gctacaatgg tcggtacaga gggttgccaa 1200
gccgcgaggt ggagctaatc ccacaaaacc gatcgtagtc cggatcgcag tctgcaactc 1260
gactgcgtga agtcggaatc gctagtaatc gcgaatcaga atgtcgcggt gaatacgttc 1320
ccgggccttg tacacaccgc ccgtcacacc atgggagtgg gttgcaccag aagtagctag 1380
tctaaccttc gggaggacgg tacca 1405
<210> 2
<211> 18
<212> DNA
<213> Artificial sequence
<220>
<223> PCR forward primer nucleotide sequence.
<400> 2
CAGAGTTTGATCCTGGCT 18
<210> 3
<211> 19
<212> DNA
<213> Artificial sequence
<220>
<223> PCR reverse primer nucleotide sequence.
<400> 3
AGGAGGTGATCCAGCCGCA 19

Claims (2)

1. An aerobic facultative autotrophic denitrifying bacterium, characterized in that it is a Korean pseudomonas (A) (B)Pseudomonas koreensis) Y5-11, deposited in China general microbiological culture Collection center, with the deposit address being No. 3 of Xilu No.1 of Beijing, Chaoyang, the date of deposit being 2018, 10 months and 29 days, and the deposit number being CGMCC No. 16651.
2. The use of an aerobic facultative autotrophic denitrifying bacterium according to claim 1, wherein said bacterium is Pseudomonas aeruginosa (Pseudomonas aeruginosa)Pseudomonas koreensis) Y5-11 was used to remove nitrate from groundwater.
CN201910073844.1A 2019-01-25 2019-01-25 Aerobic facultative autotrophic denitrifying bacterium and application thereof Active CN109517770B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201910073844.1A CN109517770B (en) 2019-01-25 2019-01-25 Aerobic facultative autotrophic denitrifying bacterium and application thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910073844.1A CN109517770B (en) 2019-01-25 2019-01-25 Aerobic facultative autotrophic denitrifying bacterium and application thereof

Publications (2)

Publication Number Publication Date
CN109517770A CN109517770A (en) 2019-03-26
CN109517770B true CN109517770B (en) 2021-12-21

Family

ID=65799726

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201910073844.1A Active CN109517770B (en) 2019-01-25 2019-01-25 Aerobic facultative autotrophic denitrifying bacterium and application thereof

Country Status (1)

Country Link
CN (1) CN109517770B (en)

Families Citing this family (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110241040B (en) * 2019-05-30 2022-03-08 山东省科学院生态研究所(山东省科学院中日友好生物技术研究中心) Korean pseudomonas and application thereof in improving organic nitrogen utilization rate of facility vegetable soil and promoting growth
CN110951658B (en) * 2020-01-15 2022-11-18 广州市微生物研究所有限公司 Pseudomonas and application thereof
CN112760268B (en) * 2021-02-09 2022-11-18 黑龙江大学 Ultraviolet-resistant bacillus and application thereof
CN112813004B (en) * 2021-02-09 2022-05-10 黑龙江大学 Ultraviolet-resistant and antioxidant immobile bacterium and application thereof
CN112877244B (en) * 2021-02-09 2022-05-17 黑龙江大学 Ultraviolet-resistant immobile bacterium and application thereof
CN113005062B (en) * 2021-03-24 2022-05-13 中国科学院成都生物研究所 Facultative ammonia oxidizing bacteria and application thereof
CN116121148A (en) * 2023-03-15 2023-05-16 浙江商达公用环保有限公司 Synchronous deoiling and denitrifying bacteria, screening, application and preparation method of microbial inoculum

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007222162A (en) * 2006-01-26 2007-09-06 Bioproject Co Ltd New bacterium belonging to genus flavobacterium and new bacterium belonging to genus pseudomonas, and feed containing them
CN103923866A (en) * 2014-04-25 2014-07-16 杭州宝晶生物股份有限公司 Pseudomonas koreensis and method for preparing mesotartaric acid or salt thereof by using same
JP2015180194A (en) * 2014-03-03 2015-10-15 国立大学法人宇都宮大学 Microbiologic agent, microorganism flock and method for producing the same
CN105586303A (en) * 2016-03-28 2016-05-18 福建农林大学 Korean pseudomonas and application thereof
CN106399183A (en) * 2016-10-19 2017-02-15 武夷学院 Aerobic denitrification bacterium and application thereof
CN109626599A (en) * 2019-01-25 2019-04-16 黑龙江大学 It is a kind of for strengthening the composite bacteria agent and its preparation method and application of low temperature low carbon-nitrogen ratio sewage denitrification effect

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP2820140B1 (en) * 2012-02-28 2018-01-10 Marrone Bio Innovations, Inc. Control of phytopathogenic microorganisms with pseudomonas sp. and substances and compositions derived therefrom
WO2019028385A1 (en) * 2017-08-04 2019-02-07 Raison, Llc Microbial inoculant compositions and methods
CN107630012A (en) * 2017-10-18 2018-01-26 武夷学院 A kind of embedding method of aerobic denitrifying bacteria

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007222162A (en) * 2006-01-26 2007-09-06 Bioproject Co Ltd New bacterium belonging to genus flavobacterium and new bacterium belonging to genus pseudomonas, and feed containing them
JP2015180194A (en) * 2014-03-03 2015-10-15 国立大学法人宇都宮大学 Microbiologic agent, microorganism flock and method for producing the same
CN103923866A (en) * 2014-04-25 2014-07-16 杭州宝晶生物股份有限公司 Pseudomonas koreensis and method for preparing mesotartaric acid or salt thereof by using same
CN105586303A (en) * 2016-03-28 2016-05-18 福建农林大学 Korean pseudomonas and application thereof
CN106399183A (en) * 2016-10-19 2017-02-15 武夷学院 Aerobic denitrification bacterium and application thereof
CN109626599A (en) * 2019-01-25 2019-04-16 黑龙江大学 It is a kind of for strengthening the composite bacteria agent and its preparation method and application of low temperature low carbon-nitrogen ratio sewage denitrification effect

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
A simple strategy for investigating the diversity and hydrocarbon degradation abilities of cultivable bacteria from contaminated soil;Maria Bučková等;《World Journal of Microbiology and Biotechnology》;20130630;第29卷(第6期);1085-1098 *
功能内生菌强化超积累植物修复重金属污染土壤的研究进展;古添源等;《生命科学》;20181130;第30卷(第11期);1228-1235 *
工业废水中高效降酚菌株的筛选;赵笛;《中国优秀硕士学位论文全文数据库工程科技Ⅰ辑》;20161016(第11期);B027-26 *

Also Published As

Publication number Publication date
CN109517770A (en) 2019-03-26

Similar Documents

Publication Publication Date Title
CN109517770B (en) Aerobic facultative autotrophic denitrifying bacterium and application thereof
Guo et al. Application potential of a newly isolated indigenous aerobic denitrifier for nitrate and ammonium removal of eutrophic lake water
CN110656059B (en) Pseudomonas strain YG8, seed liquid and preparation method and application thereof
CN108977399B (en) Alcaligenes faecalis and application thereof
CN109055282B (en) Novel Klebsiella pneumoniae strain and separation method and application thereof
CN105733998B (en) Efficient denitrification strain with heterotrophic nitrification and aerobic denitrification capabilities
CN109536426B (en) Psychrophile and application thereof
Nakagawa et al. Nitrosomonas stercoris sp. nov., a chemoautotrophic ammonia-oxidizing bacterium tolerant of high ammonium isolated from composted cattle manure
CN109456926B (en) Microbial agent containing halophilic denitrifying bacteria YL5-2 and application thereof
US20220380240A1 (en) Novosphingobium sp. sjb007 and application thereof in removal of phosphorus from wastewater
CN110283739B (en) Salt-tolerant denitrifying bacterium and application thereof
CN114703095B (en) Pseudomonas adulthood and application thereof in field of sewage and wastewater purification
CN112195126B (en) Denitrification strain, microbial agent and application
CN112251387B (en) Denitrifying bacteria and application thereof
CN115386520B (en) Rhodococcus pyridine-philic RL-GZ01 strain and application thereof
CN110591947A (en) Heterotrophic ammonia oxidizing bacteria and application thereof
CN113234636A (en) Denitrifying bacterium pseudomonas strain F1 and application thereof
CN109722394B (en) Pseudomonas arsenic oxide strain and application thereof
CN109534518B (en) High-salinity wastewater biofilm treatment process using halophilic bacteria YL5-2
CN115948288B (en) Aerobic high-efficiency denitrification compound flora and application thereof
CN111979138A (en) Heterotrophic nitrification aerobic denitrifying bacterium Y15 and application thereof
CN116004480A (en) Deep sea bacteria capable of heterotrophic aerobic growth and having autotrophic sulfur oxidation denitrification function and application thereof
CN109666613B (en) Facultative autotrophic rhizobium with nitrate reduction ferrous oxidation function and application thereof
CN110468066B (en) Aerobic denitrifying strain and application thereof
CN114292798A (en) Anaerobic denitrifying bacterium and application thereof in riverway water body restoration

Legal Events

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