CN108865940A - One plant of heterotrophic nitrification-aerobic denitrification bacillus and its composite bacteria preparation - Google Patents

One plant of heterotrophic nitrification-aerobic denitrification bacillus and its composite bacteria preparation Download PDF

Info

Publication number
CN108865940A
CN108865940A CN201810782000.XA CN201810782000A CN108865940A CN 108865940 A CN108865940 A CN 108865940A CN 201810782000 A CN201810782000 A CN 201810782000A CN 108865940 A CN108865940 A CN 108865940A
Authority
CN
China
Prior art keywords
bacillus
bsxs
bacterium
powder
bbhs
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.)
Granted
Application number
CN201810782000.XA
Other languages
Chinese (zh)
Other versions
CN108865940B (en
Inventor
田相利
赵坤
李海东
蒋雯雯
宋君
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.)
Ocean University of China
Original Assignee
Ocean University of China
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 Ocean University of China filed Critical Ocean University of China
Priority to CN201810782000.XA priority Critical patent/CN108865940B/en
Publication of CN108865940A publication Critical patent/CN108865940A/en
Application granted granted Critical
Publication of CN108865940B publication Critical patent/CN108865940B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

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
    • C12R2001/07Bacillus
    • AHUMAN NECESSITIES
    • A23FOODS OR FOODSTUFFS; TREATMENT THEREOF, NOT COVERED BY OTHER CLASSES
    • A23KFODDER
    • A23K10/00Animal feeding-stuffs
    • A23K10/10Animal feeding-stuffs obtained by microbiological or biochemical processes
    • A23K10/16Addition of microorganisms or extracts thereof, e.g. single-cell proteins, to feeding-stuff compositions
    • A23K10/18Addition of microorganisms or extracts thereof, e.g. single-cell proteins, to feeding-stuff compositions of live microorganisms
    • AHUMAN NECESSITIES
    • A23FOODS OR FOODSTUFFS; TREATMENT THEREOF, NOT COVERED BY OTHER CLASSES
    • A23KFODDER
    • A23K50/00Feeding-stuffs specially adapted for particular animals
    • A23K50/80Feeding-stuffs specially adapted for particular animals for aquatic animals, e.g. fish, crustaceans or molluscs
    • 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
    • C02F3/30Aerobic and anaerobic processes
    • C02F3/302Nitrification and denitrification treatment
    • 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
    • C12N1/20Bacteria; 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

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Microbiology (AREA)
  • Health & Medical Sciences (AREA)
  • Organic Chemistry (AREA)
  • Zoology (AREA)
  • Biotechnology (AREA)
  • Bioinformatics & Cheminformatics (AREA)
  • Genetics & Genomics (AREA)
  • Wood Science & Technology (AREA)
  • Polymers & Plastics (AREA)
  • Biochemistry (AREA)
  • Biomedical Technology (AREA)
  • General Engineering & Computer Science (AREA)
  • General Health & Medical Sciences (AREA)
  • Animal Husbandry (AREA)
  • Tropical Medicine & Parasitology (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Virology (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Food Science & Technology (AREA)
  • Hydrology & Water Resources (AREA)
  • Medicinal Chemistry (AREA)
  • Insects & Arthropods (AREA)
  • Birds (AREA)
  • Marine Sciences & Fisheries (AREA)
  • Molecular Biology (AREA)
  • Physiology (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Fodder In General (AREA)

Abstract

The invention patent belongs to microorganism and its application field more particularly to one plant of heterotrophic nitrification-aerobic denitrification bacillus BSXS-1602;It further relates to more than one and states heterotrophic nitrification-aerobic denitrification bacillus BSXS-1602 composite bacteria preparation as main component;The invention further relates to more than one to state heterotrophic nitrification-aerobic denitrification bacillus BSXS-1602 Mixed Microbes powder as main component.Heterotrophic nitrification-aerobic denitrification bacillus of the invention is bacillus BSXS-1602, has carried out preservation in China General Microbiological culture presevation administrative center on June 15th, 2018, deposit number is:CGMCC NO.15950.Bacillus BSXS-1602 of the invention is separated from sea water culture environment, is had efficient heterotrophic nitrification-aerobic denitrification capability, can be used to aquaculture water environment.

Description

One plant of heterotrophic nitrification-aerobic denitrification bacillus and its composite bacteria preparation
Technical field
The invention patent belongs to microorganism and its application field more particularly to one plant of heterotrophic nitrification-aerobic denitrification gemma Bacillus BSXS-1602;It further relates to more than one and states heterotrophic nitrification-aerobic denitrification bacillus BSXS-1602 be main component Composite bacteria preparation;It is main for stating heterotrophic nitrification-aerobic denitrification bacillus BSXS-1602 the invention further relates to more than one The Mixed Microbes powder of ingredient.
Background technique
Polluted by nitrogen is to seriously threaten the existence of aquatile one of an important factor for causing cultivation water to deteriorate.Biology is de- Nitrogen because its have many advantages, such as it is economical, efficiently, environmental protection due to be increasingly becoming research hotspot in recent years.Traditional biological denitrificaion usually wraps Containing two parts, the first step is nitrification, i.e., Autotrophic nitrification bacterium carries out nitrogen conversion under aerobic condition:NH4 +-N→NO2 --N →NO3 --N;Second step is that allotrophic nitrobacteria carries out nitrogen conversion under anaerobic:NO3 --N→NO2 -- N → NO, N2O→N2。 The condition as required for the two stages is completely different, and traditional biological denitrification system must include two individual bodies System causes denitrogenation cost to increase.Studies have shown that allotrophic nitrobacteria can will cultivate while being grown using carbon source Nitrogenous compound in water body is converted into NH by nitrification2OH、NO2 -- N or NO3 -- N etc.;At the same time, most of thin Bacterium can also carry out aerobic denitrification simultaneously, by NO2 -- N or NO3 -- N is converted into NO, N2O and N2Equal gases.Paracoccu Denitrificans (being initially named as Thiosphaera pantotropha) be first strain be reported have aerobic denitrification The bacterial strain of effect, can be by NO3 -- N or NO2 -- N denitrification is N2.Hereafter, more new aerobic denitrifying bacterias are separated And research, such as Thiosphaerapantotropha, pseudomonas (Pseudomonas), Bacillus foecalis alkaligenes (Alcaligenes faecalis), bacillus (Bacillus) etc..
Recent study shows that bacillus has stronger nitrification and denitrification performance, can effectively remove cultivation NH in water body4 +- N and NO2 -- N reduces NH4 +- N and NO2 -Toxic action of the substances such as-N to aquaculture organism.That reports at present is big Part heterotrophic nitrification-aerobic denitrification strain isolation is isolated from sea-farming from soil, sewage disposal system and biological filter membrane etc. The rarely seen report of the bacterial strain of environment, the living environment difference of bacterial strain cause its adaptability and nitrogen removal performance there are biggish difference, because There is this separation screening from sea water culture environment the bacterial strain of efficient denitrification ability to be particularly important.
Summary of the invention
An object of the present invention is that separation screening one kind has efficient heterotrophic nitrification-good from sea water culture environment The bacillus of oxygen denitrification capability.
In order to solve the above-mentioned technical problem, the present invention uses following technical scheme, a kind of heterotrophic nitrification-aerobic denitrification bud Spore bacillus, be bacillus BSXS-1602, on June 15th, 2018 China General Microbiological culture presevation administrative center into Preservation is gone, deposit number is:CGMCC NO.15950.
The bacillus BSXS-1602 removal capacity mainly includes to NH4 +- N and NO2 -In terms of the removal of-N, the bacterial strain It is separation screening from the denitrifying bacillocin of litopenaeus vannamei (Litopenaeus vannamei) cultivating pool bed mud, is named as BSXS-1602 is identified as bacillus subtilis (Bacillus subtilis).
The invention also discloses a kind of above-mentioned bacillus BSXS-1602 to purify water, remove NH4 +- N and NO2 --N And the application in aquaculture water environment conditioning.
One probiotics bacterial strain success be applied to production practices, not only with bacterial strain itself it is higher conversion and denitrogenation Can be related, it is also most important to the adaptability of environment.Result of study shows that bacillus BSXS-1602 of the invention has Higher heterotrophic nitrification-aerobic denitrification capability, wider to the adaptation range of C/N, salt tolerant range is wide, has stronger oxytolerant Property, there is good potential using value in aquaculture water environment conditioning.
A kind of bacterium powder of above-mentioned bacillus BSXS-1602, preparation method are as follows:Bacillus BSXS-1602 is living Change, expand culture, through 28 DEG C of liquid state fermentations, thalline were collected by centrifugation by 8000rpm, bentonite is added as carrier, by thallus with it is swollen Profit soil stirs evenly, and the bacterium powder that bacterium amount is 100~50,000,000,000/g is made in 45 DEG C of drying.
The invention also discloses a kind of above-mentioned bacillus BSXS-1602 bacterium powder answering as aquatic animal feed additive With, and regulation water quality application add when the bacillus BSXS-1602 bacterium powder is as aquatic animal feed additive Dosage is the 0.05-0.2% of feeding quality.Bacillus BSXS-1602 bacterium powder of the invention facilitates storage and use, can promote Into the appetite of aquatic livestock, when feeding litopenaeus vannamei as feed addictive, feed coefficient can be effectively reduced, is promoted all The shore prawn that receives growth.
It is a further object of the present invention to provide one kind with bacillus BSXS-1602 composite bacteria preparation as main component, The composite bacteria preparation is by bacillus BSXS-1602, white tail feather bacillus (Bacillus baekryungensis) BBHS-01 is with 10~12:1 bacterial population ratio is combined.The white tail feather gemma bar BBHS-01, on December 7th, 2012 Preservation, preservation address have been carried out in China Committee for Culture Collection of Microorganisms's common micro-organisms collection:Court of Beijing The road Yang Qu great Tun, Institute of Microorganism, Academia Sinica, deposit number are:CGMCC NO.6939.
More than one are stated bacillus BSXS-1602 composite bacteria preparation as main component and are purifying water, removing NH4 +-N And NO2 -Application in-N and aquaculture water environment conditioning.
The experimental results showed that bacillus BSXS-1602 and Bai Ling bacillus BBHS-01 is without antagonism, by gemma bar Bacterium BSXS-1602, white tail feather bacillus BBHS-01 are with 10~12:1 bacterial population ratio compound tense, bacillus BSXS-1602 It quickly can well be grown with white tail feather bacillus BBHS-01, it is bacillus BSXS-1602, BBHS-01 pairs of tail feather bacillus white The removal effect aspect of nitrogen pollutant has synergistic effect, is embodied in:Bacillus BSXS-1602, white tail feather bacillus BBHS-01 is with 10~12:The compound obtained composite bacteria preparation of 1 bacterial population ratio can effectively remove NH4 +- N and NO2 -- N improves breeding environment, and under dose profile, complex enzyme formulation is to NH4 +- N and NO2 -The removal rate of-N is significantly higher than arbitrarily A kind of removal efficiency of single strain.
A kind of Mixed Microbes powder as main component with bacillus BSXS-1602, preparation method are as follows:By gemma bar Bacterium BSXS-1602 and Bai Ling bacillus BBHS-01 is activated respectively, is expanded culture, then respectively through 28 DEG C of liquid state fermentations, then will Bacillus BSXS-1602 and Bai Ling bacillus BBHS-01 is according to 10~15:1 bacterial population ratio mixing, 8000rpm from The heart collects thallus, and bentonite and xanthan gum is added as carrier, thallus and bentonite, xanthan gum are stirred evenly, 45 DEG C of drying, The bacterium powder that total bacterium amount is 100~50,000,000,000/g is made.
Further, the carrier is bentonite and xanthan gum according to 5:1 mass ratio mixes.By using swelling Soil and xanthan gum can load bacillus BSXS-1602 and Bai Ling bacillus BBHS-01 as carrier well, make this The Mixed Microbes powder of invention is not easy to be broken up by water flow, and then is conducive to bacillus BSXS-1602 and Bai Ling bacillus BBHS- The performance of 01 synergistic effect.
The invention also discloses more than one to state application of the Mixed Microbes powder as feed addictive, and regulates and controls answering for water quality With when the Mixed Microbes powder is as feed addictive, additive amount is the 0.01~0.1% of feeding quality.
Mixed Microbes powder of the invention can promote the appetite of aquatic livestock, when feeding aquatic livestock as feed addictive, energy Improve aquatic livestock enteron aisle structure of community, than as can improve stichopus japonicus and litopenaeus vannamei enteron aisle structure of community, can be effective Reduction feed coefficient, promote Growth of Litopenaeus vannamei, furthermore Mixed Microbes powder of the invention facilitate storage and it is easy to use.
Compared with prior art, the beneficial effects of the invention are as follows:
(1) by being enriched with to litopenaeus vannamei cultivating pool bed mud, screening has efficient heterotrophic nitrification-for this research The bacillus BSXS-1602 of aerobic denitrification capability, according to the morphological feature of bacterial strain, physio-biochemical characteristics and 16S rDNA Sequence and specific sequence compare analysis, and bacterial strain BSXS-1602 is accredited as bacillus subtilis (Bacillus subtilis).One probiotics bacterial strain success be applied to production practices, not only with the higher conversion of bacterial strain itself and denitrogenation Performance is related, also most important to the adaptability of environment.The present invention passes through analysis the varying environment factor (carbon source, C/N (quality Than), pH, salinity and revolving speed) influence to bacterial strain BSXS-1602 heterotrophic nitrification-aerobic denitrification characteristic, find at 28 DEG C of temperature Under, bacterial strain BSXS-1602 is respectively glucose, C/N 18, pH value 7.5, salinity 30 ‰ and revolving speed 160rpm condition in carbon source Under heterotrophic nitrification-aerobic denitrification capability with higher.On this basis, bacterial strain BSXS-1602 heterotrophism nitre is had studied respectively Change and aerobic denitrifying optimum reaction condition.Orthogonal experiment results show when with NH4When Cl is nitrogen source, bacterial strain BSXS- 1602 best nitration condition is that C/N 10, pH value 9.0, salinity 10 ‰ and revolving speed are 160rpm respectively.When with NaNO2For nitrogen source When, the best Denitrification Conditions of bacterial strain BSXS-1602 are that C/N 10, pH value 6.0, salinity 30 ‰ and revolving speed are 160rpm respectively. To sum up, bacillus BSXS-1602 heterotrophic nitrification-aerobic denitrification capability with higher of the invention, to the adaptation model of C/N It encloses relatively extensively, salt tolerant range is wide, has stronger oxygen resistence, has potential application in aquaculture water environment conditioning.
(2) bacillus BSXS-1602, white tail feather bacillus BBHS-01 are with 10~12:The compound institute of 1 bacterial population ratio Composite bacteria preparation obtained can effectively remove NH4 +- N and NO2 -- N improves breeding environment, under dose profile, complex enzyme Preparation is to NH4 +- N and NO2 -The removal rate of-N is significantly higher than the removal efficiency of any one single strain.
(3) the bacterium powder of bacillus BSXS-1602 and with bacillus BSXS-1602 Mixed Microbes powder as main component The appetite that can promote aquatic livestock when feeding aquatic livestock as feed addictive, can effectively reduce feed coefficient, promote Growth of Litopenaeus vannamei, furthermore Mixed Microbes powder of the invention facilitate storage and it is easy to use.
Detailed description of the invention
Fig. 1 constructs the phylogenetic tree of bacterial strain BSXS-1602 based on 16S rDNA sequence;
Fig. 2 is the phylogenetic tree based on 16S rDNA gene order of white tail feather bacillus BBHS-01 and related strain.
Specific embodiment
Embodiment below facilitates a better understanding of the present invention, but does not limit the present invention.Experiment in following embodiments Method is unless otherwise specified conventional method.
Sample source:The bed mud sample in prawn culturing pond used in this research picks up from Jiangsu Province in July, 2014 Three prawn bait throwing in of the Jia Xin aquatic products development corporation, Ltd. of the Agricultural Industrialized Parks Ganyu County (34 ° of 58 ' N, 119 ° of 20 ' E) cultivate Pond (28 DEG C of temperature).
Main agents and instrument:The Primary Chemical that this research uses is purchased from the limited public affairs of Chinese medicines group chemical reagent Department.It is that analysis is pure except specified otherwise;PCR reagent is purchased from complete biological (TransGen Biotech) company of scholar's gold in Beijing, bacterium Universal primer and specific sequence amplimer are closed by raw work bioengineering (Sangon Biotech) Co., Ltd in Shanghai At.Key instrument used includes:- 80 DEG C of ultra low temperature freezers (SANYO Electric Co., Ltd.Japan);Electronic balance (METTLED TOLEDO Corp.Shanghai,China);AIR TECH superclean bench (ten thousand net safe and sound companies of group); SPX type Intelligent biochemistry incubator (Ningbo Jiangnan instrument plant);(Chinese Harbin City east joins electronic technology to HZQ-Q constant-temperature table Development corporation, Ltd.);556 multi-parameter water quality measuring instrument of YSI (YSI Incorporated, USA);DR2700 type spectrophotometric It counts (HACH Incorporated, USA);High speed freezing centrifuge (Hitachi Koki Co., Ltd.Japan).
Culture medium
Culture medium used in this research mainly includes:
(1) enriched medium:(NH4)2SO4 2.0g、MgSO4 0.10g、NaH2PO4.2H2O 0.26g、K2HPO4 0.5g、 CaCO3 1.0g、FeSO4.7H2O 0.183g, glucose 5g, KNO2 1.0g、NH4Cl 0.5g, yeast extract 0.02g, seawater 1000mL,pH 7.5;Separation plate is the agar that 2.0% (w/v) is added in above-mentioned enriched medium;
(2) 2216E culture medium:Tryptone 6.0g, yeast extract 2.0g, seawater 1000mL, pH 7.5.2216E points It is the agar that 2.0% (w/v) is added in above-mentioned enriched medium from plate;
The nitrogen removal performance detection of bacterial strain uses the aquaculture simulated wastewater manually prepared, and mainly includes:Basic test liquid, Heterotrophic nitrification culture medium (HNM) and nitrite denitrification culture medium (NDM).Wherein,
Basic test liquid:NH4Cl 0.1605g、NaNO20.05g, glucose 2.475g, seawater 1000mL, pH 7.5;
Heterotrophic nitrification culture medium (HNM):NH4Cl 0.1605g, glucose 2.0808g, seawater 1000mL, pH 7.5;
Nitrite denitrification culture medium (NDM):NaNO20.207g, glucose 2.0808g, seawater 1000mL, pH 7.5;
Above-mentioned enriched medium and manual simulation's aquiculture waste water are handled through high pressure sterilization using preceding.
The separation and identification of 1 bacterial strain bacillus BSXS-1602 of embodiment
1, the separation and screening of Bacillus strain
Bed mud sample after taking prawn culturing pond to premix carries out gradient dilution with antiseptic sea water, and sufficiently oscillation is quiet after mixing It sets.Supernatant is taken in sterile centrifugation tube and places it in heating water bath 20min in 90 DEG C of water-baths.Water intaking bath treated supernatant Liquid is seeded in the 250mL conical flask containing enriched medium.By one star of conical flask continuous oscillation culture after inoculation Phase obtains initial enrichment bacterium solution.According to 1:Initial enrichment bacterium solution is seeded to and continues to train in enriched medium by 10 inoculative proportion A week is supported, repeatedly domestication 6 periods of culture.Last time enrichment bacterium solution is taken, the separation and purifying of bacterial strain are carried out. Bacterial strain after purification is subjected to Gram's staining and spore staining.Select Gram's staining and bacterium that spore staining is positive Strain carries out the pathogenic detection of bacterial strain using blood plate method, chooses and further studied there is no pathogenic bacterial strain.Utilize base Plinth test fluid further screens the above-mentioned bacterial strain filtered out, selects the bacterial strain with nitrification and denitrification ability.
Water-bath, Gram's staining and spore staining, preliminary screening, which are carried out, by the bacterial strain filtered out to acclimating obtains 5 Bacillus;Then by removing liquid NH to basis with bacterial strain4 +- N and NO2 -The removal ability of-N is foundation, is further screened Obtaining 1 plant has high efficiency nitrification-denitrification capability bacterial strain, as BSXS-1602.
2, the identification of bacterial strain
The measurement of bacterial strain physio-biochemical characteristics:The project of identification mainly includes form, Gram's staining, the gemma dye of bacterial strain Color, methyl red, V-P measurement, oxidizing ferment, catalase, amylolytic enzyme, lipase, lysozyme, nitrite reductase, Western-style lemon Lemon hydrochlorate, glucose fermentation, mannitol, gelatin liquefaction, anaerobic growth, dynamic culture base and H2S。
The 16S rDNA gene order (1460bp) and NCBI database sequence of bacterial strain BSXS-1602 after sequencing amplification Be compared, chosen based on 16S rDNA sequence homology related strain gene order phylogenetic tree construction (see Fig. 1, Wherein BSXS-1602 is bacterial strain bacillus BSXS-1602 of the invention).In conjunction with bio-chemical characteristics result and 16S rDNA Sequence Identification can determine that bacterial strain BSXS-1602 is bacillus subtilis.
3, the morphological observation of bacterial strain BSXS-1602
Under an optical microscope, bacterial strain BSXS-1602 is in rod-short, has flagellum, can move.By Gram's staining and The bacterial strain of spore staining is under an optical microscope Gram-positive, and spore staining is uniform.By the bacterial strain BSXS- of purifying 1602 be placed in 28 DEG C of biochemical cultivation case under the conditions of cultivate 24 hours after, bacterium colony on 2216E plate is milky, flat, impermeable It is bright, edge is irregular.
4, Physiology and biochemistry qualification result
The Physiology and biochemistry of bacterial strain BSXS-1602 and type strain bacillus subtilis CGMCC1.3358 the results are shown in Table 1.
The Physiology and biochemistry result of table 1 bacterial strain BSXS-1602 and bacillus subtilis CGMCC1.3358
Remarks:"+" represents the positive;"-" represents feminine gender.
5, the influence of varying environment factor pair bacterial strain bacillus BSXS-1602
By the analysis varying environment factor (carbon source, C/N (mass ratio), pH, salinity and revolving speed) to bacterial strain BSXS-1602 The influence of heterotrophic nitrification-aerobic denitrification characteristic finds that at 28 DEG C of temperature, bacterial strain BSXS-1602 is respectively grape in carbon source Heterotrophic nitrification-aerobic denitrification with higher under the conditions of sugar, C/N 18, pH value 7.5, salinity 30 ‰ and revolving speed 160rpm Energy.Result of study shows bacterial strain heterotrophic nitrification-aerobic denitrification capability with higher, in aquaculture water environment conditioning In have potential application.
The main feature of the white tail feather bacillus BBHS-01 of embodiment 2 and its removal of water pollutant is tested
1. the main feature of white tail feather bacillus BBHS-01 is as follows:
(1) morphological feature:
Form be it is rod-shaped, can move, can produce gemma, binary fission reproduction, thallus is individually, two-by-two or the gathering of short chain.
(2) physiological and biochemical property:
Bacterial strain Gram-positive, spore staining is positive, grease hydrolysis enzyme positive, Starch Hydrolysis enzyme positive, contacts enzyme positive, V-P negative, glucose oxidative fermentation produce gas, the gelatin positive, Lactose-positive, the maltose positive, mannitol feminine gender, sweet dew Sugared positive, sucrose feminine gender, arabinose is negative, xylose is negative.
(3) bacterial strain is identified
Bacterium is finally determined according to the phylogenetic tree of the 16S rDNA of white tail feather bacillus BBHS-01 and related strain building Strain is the bacterium of white tail feather bacillus (see Fig. 2, wherein BBHS-01 is the white tail feather bacillus of bacterial strain of the invention).
2. white tail feather bacillus BBHS-01 tests the removal of water pollutant:
(1) prawn feed solid plate growing state detects:
White tail feather bacillus BBSH-01 is separated from the bed mud of prawn culturing pond, and (deposit number is: CGMCC NO.6939), in 28 ± 1 DEG C of shrimp feed mediums in 20g/L, (commercially available prawn feed 20g is ground into fine powder to the bacterial strain, sterilizing Chen Haishui 1000mL impregnates centrifuging and taking supernatant after 48h, adds 25 g of agar, adjusts 7.8,121 DEG C of pH, and sterilize 20min) on growing way Good, growth rapidly, cultivates colony diameter for 24 hours up to 2mm or so.
(2) the removal effect detection of prawn feed leachate:
1) white tail feather bacillus BBHS-01 tests the removal effect of prawn feed leachate
Experiment removal liquid used:It is ground into fine powder for commercially available prawn feed 20g, sterilize Chen Haishui 1000mL, after impregnating 48h Centrifuging and taking supernatant adds sodium nitrite 0.058g, adjusts pH 7.8, is distributed into 100mL/ bottles, and in 121 DEG C, sterilize 20min.
The object of the activation culture for 24 hours 8000rpm of white tail feather bacillus BBHS-01 is centrifuged 10min, is washed with sterile saline Agent precipitates thallus, and is diluted to containing 1 × 106Then bacterium solution is added to the prawn of 100mL by the bacterium solution of cfu/mL in 1% ratio Bait removes in liquid, and 28 ± 1 DEG C, shaken cultivation 5d under 160rpm, daily timing sampling measure the ammonia nitrogen (NH in sample liquid4 +- N), cultured water (NO2 -- N) content, OD600, using be not added with bacterial strain as control treatment, each processing sets 3 repetitions.
2) experimental result
Experimental result is shown in Table 2 respectively.The experimental results showed that:White tail feather bacillus BBHS-01 is to prawn feed removal liquid tool Have apparent removal effect, during the experiment with the growth of the bacterial strain, can significantly remove inorganic nitrogen in bait removal liquid at Point, wherein to NH4 +-N、NO2 -The highest removal rate of-N is respectively 60.34%, 92.40%.
The white tail feather bacillus BBHS-01 of table 2 is in different incubation times to the removal effect of bait leachate
The antagonistic experiment of 3 bacillus BSXS-1602 of embodiment and white tail feather bacillus BBHS-01
It takes bacillus BSXS-1602, white tail feather bacillus BBHS-01 to cross in 2216E solid medium respectively, is placed in After 28 DEG C of cultures for 24 hours, picks them separately single colonie and carry out cross scribing line on 2216E solid medium, by the plate of scribing line in 28 DEG C culture for 24 hours after, check strain growth situation, antagonistic experiment scribing line cultivation results show that antagonism is not present in two bacterial strains.
4 bacillus BSXS-1602 of embodiment tests the removal of water pollutant
(1) prawn feed solid plate growing state detects:
In 28 ± 1 DEG C of shrimp feed mediums in 20g/L, (commercially available prawn feed 20g is ground bacillus BSXS-1602 At fine powder, sterilize Chen Haishui 1000mL, impregnates centrifuging and taking supernatant after 48h, adds agar 25g, adjusts 7.8,121 DEG C of pH, sterilizing Growing way is good on 20min), and growth rapidly, cultivates colony diameter for 24 hours up to 2mm or so.
(2) the removal effect detection of prawn feed leachate:
1) bacillus BSXS-1602 tests the removal effect of prawn feed leachate
Testing test fluid used is:Commercially available prawn feed 20g is ground into fine powder, and sterilize Chen Haishui 1000mL, impregnates 48h Afterwards, centrifuging and taking supernatant adds sodium nitrite 0.058g, adjusts pH 7.8, is distributed into 100mL/ bottles, and in 121 DEG C, sterilize 20min.
The object of the activation culture for 24 hours 8000rpm of bacillus BSXS-1602 is centrifuged 10min, with sterile saline lotion Thallus is precipitated, and is diluted to containing 1 × 106Then bacterium solution is added to the prawn bait of 100mL by the bacterium solution of cfu/mL in 1% ratio Expect in leachate, 28 DEG C, 160rpm continuous oscillation culture 5d, daily timing sampling, measures the ammonia nitrogen (NH in sample liquid4 +-N)、 Cultured water (NO2 -- N) content, thalli growth amount, bacterium is not added as control treatment, each processing sets 3 repetitions.
2) experimental result
Experimental result is shown in Table 5 respectively.The experimental results showed that:Bacillus BSXS-1602 is in prawn feed leachate NH4 +- N and NO2 -- N has apparent removal effect, during the experiment with the growth of the bacterial strain, can significantly remove bait leaching Inorganic nitrogen component in liquid, wherein to NH4 +- N and NO2 -The highest removal rate of-N is respectively 52.35%, 97.23%.
5 bacillus BSXS-1602 of table is in different incubation times to the removal effect of bait leachate
5 composite bacteria preparation of embodiment tests the removal of water pollutant
The composite bacteria preparation of the present embodiment is by bacillus BSXS-1602, white tail feather bacillus BBHS-01 with 10:1 Bacterial population ratio be combined.
Testing test fluid used is:Commercially available prawn feed 20g is ground into fine powder, and sterilize Chen Haishui 1000mL, after impregnating 48h Centrifuging and taking supernatant adds sodium nitrite 0.058g, adjusts pH 7.8, is distributed into 100mL/ bottles, and in 121 DEG C, sterilize 20min.
Bacillus BSXS-1602 and Bai Ling bacillus BBHS-01 is cultivated through activation culture for 24 hours, expansion respectively, then Respectively through 28 DEG C of liquid state fermentations, then by bacillus BSXS-1602 and Bai Ling bacillus BBHS-01 according to 10:1 bacterium Number ratio mixing, precipitates thallus with sterile saline lotion, will mix mycelium dilution, and it is 1 × 10 that concentration, which is made,6Cfu/mL's Then bacterium solution is added to bacterium solution in the prawn feed leachate of 100 mL in 1% ratio, 28 DEG C, 160rpm continuous oscillation training 5d is supported, daily timing sampling measures the ammonia nitrogen (NH in sample liquid4 +- N), cultured water (NO2 -- N) content, thalli growth amount, Bacterium is not added as control treatment, each processing sets 3 repetitions.Experimental result is shown in Table 6 respectively.The experimental results showed that:Gemma bar Bacterium BSXS-1602 is to the NH in prawn feed leachate4 +- N and NO2 -- N have apparent removal effect, during the experiment with The growth of the bacterial strain can significantly remove the inorganic nitrogen component in bait removal liquid, wherein to NH4 +- N and NO2 -The highest of-N removes Rate is respectively 93.66%, 100%.
6 composite bacteria preparation of table is in different incubation times to the removal effect (1~5d) of bait removal liquid
Facilitation of the 6 bacillus BSXS-1602 bacterium powder of embodiment to Growth of Litopenaeus vannamei
The bacterium powder of the bacillus BSXS-1602 of the present embodiment, preparation method are as follows:Bacillus BSXS-1602 is living Change, expand culture, through 28 DEG C of liquid state fermentations, thalline were collected by centrifugation by 8000rpm, bentonite is added as carrier, by thallus with it is swollen Profit soil stirs evenly, and the bacterium powder that bacterium amount is 100~50,000,000,000/g is made in 45 DEG C of drying.
The bacillus BSXS-1602 bacterium powder of the present embodiment is pressed to 0.05%, 0.1%, 0.15%, 0.2% matter respectively Amount percentage is respectively added in prawn mixed feed, and not add the processing group of bacterium powder as a control group, each processing is set 3 times It repeats, continuous feeding litopenaeus vannamei (prawn original body mass is 0.6 ± 0.08g) 45 days, at the end of experiment, addition 0.05% The processing group litopenaeus vannamei average growth rate of bacillus BSXS-1602 bacterium powder is 283.3%, feed coefficient 1.65;Add The processing group litopenaeus vannamei average growth rate for adding 0.1% bacillus BSXS-1602 bacterium powder is 297.5%, and feed coefficient is 1.57;The processing group litopenaeus vannamei average growth rate for adding 0.15% bacillus BSXS-1602 bacterium powder is 318.4%, bait Expect that coefficient is 1.51;The processing group litopenaeus vannamei average growth rate for adding 0.2% bacillus BSXS-1602 bacterium powder is 318.9%, feed coefficient 1.48;Control group litopenaeus vannamei average growth rate is 261.8%, feed coefficient 2.04.
Bacillus BSXS-1602 bacterium powder of the invention facilitates storage and use, can promote the appetite of aquatic livestock, as When feed addictive feeds litopenaeus vannamei, feed coefficient can be effectively reduced, promotes Growth of Litopenaeus vannamei.
Embodiment 7 is with Mixed Microbes powder bacillus BSXS-1602 as main component to the rush of Growth of Litopenaeus vannamei Into effect
The Mixed Microbes powder as main component with bacillus BSXS-1602 of the present embodiment, preparation method are as follows:It will Bacillus BSXS-1602 and Bai Ling bacillus BBHS-01 is activated respectively, is expanded culture, then respectively through 28 DEG C of liquid state fermentations, Then by bacillus BSXS-1602 and Bai Ling bacillus BBHS-01 according to 15:1 bacterial population ratio mixing, 8000rpm Thalline were collected by centrifugation, and bentonite and xanthan gum is added as carrier, and (mass ratio of bentonite and xanthan gum is 5:1), by thallus with Bentonite, xanthan gum stir evenly, and the bacterium powder that total bacterium amount is 100~50,000,000,000/g is made in 45 DEG C of drying.
The Mixed Microbes powder of the present embodiment is pressed to 0.01%, 0.05%, 0.08%, 0.1% mass percent difference respectively It is added in prawn mixed feed, not add the processing group of Mixed Microbes powder as a control group, each processing sets 3 repetitions, even Continuous feeding litopenaeus vannamei (prawn original body mass is 0.6 ± 0.08g) 45 days, at the end of experiment, adds 0.01% Mixed Microbes powder Processing group litopenaeus vannamei average growth rate be 281.7%, feed coefficient 1.68;Add the processing of 0.05% Mixed Microbes powder Group litopenaeus vannamei average growth rate is 299.3%, feed coefficient 1.59;The processing group for adding 0.08% Mixed Microbes powder all is received Shore prawn average growth rate is 317.2%, feed coefficient 1.48;Add the processing group litopenaeus vannamei of 0.1% Mixed Microbes powder Average growth rate is 320.2%, feed coefficient 1.45;Control group litopenaeus vannamei average growth rate is 261.8%, bait system Number is 2.04.
Mixed Microbes powder of the invention facilitates storage and use, can promote the appetite of aquatic livestock, throws as feed addictive When feeding litopenaeus vannamei, feed coefficient can be effectively reduced, promotes Growth of Litopenaeus vannamei.
The above is only a preferred embodiment of the present invention, it should be pointed out that:For the ordinary skill people of the art For member, without departing from the principle of the present invention, several improvement can also be made, these improvement should be regarded as guarantor of the invention Protect range.

Claims (10)

1. a kind of heterotrophic nitrification-aerobic denitrification bacillus is bacillus BSXS-1602, on June 15th, 2018 in State's General Microbiological Culture preservation administrative center has carried out preservation, and deposit number is:CGMCC NO.15950.
2. a kind of bacillus BSXS-1602 described in claim 1 is in removal NH4 +- N and NO2 -- N and aquaculture water ring Application in the regulation of border.
3. a kind of bacterium powder made of bacillus BSXS-1602 described in claim 1.
4. a kind of preparation method of bacterium powder as claimed in claim 3, which is characterized in that include the following steps:By bacillus BSXS-1602 activation expands culture, and through 28 DEG C of liquid state fermentations, 8000rpm is collected by centrifugation bacterium mud, bentonite is added as carrier, Bacterium mud and bentonite are stirred evenly, the bacterium powder that bacterium amount is 100~50,000,000,000/g is made in 45 DEG C of drying.
5. a kind of application of bacterium powder as claimed in claim 3 as aquatic animal feed additive, and the application of regulation water quality.
6. one kind is with bacillus BSXS-1602 composite bacteria preparation as main component described in claim 1, feature exists In the composite bacteria preparation is by bacillus BSXS-1602, white tail feather bacillus BBHS-01 with 10~12:1 bacterial population Ratio is combined;The white tail feather bacillus BBHS-01 (Bacillus baekryungensis), on December 7th, 2012 Preservation is carried out in China Committee for Culture Collection of Microorganisms's common micro-organisms collection, deposit number is:CGMCC NO.6939。
7. a kind of composite bacteria preparation as claimed in claim 6 is in degradation NH4 +- N and NO2 -In-N and aquaculture water environment conditioning Application.
8. a kind of Mixed Microbes powder as main component with bacillus BSXS-1602 described in claim 1, feature exist In preparation method is as follows:Bacillus BSXS-1602 and Bai Ling bacillus BBHS-01 is activated respectively, expands culture, then Respectively through 28 DEG C of liquid state fermentations, then by bacillus BSXS-1602 and Bai Ling bacillus BBHS-01 according to 10~15:1 The mixing of bacterial population ratio, thalline were collected by centrifugation by 8000rpm, and bentonite and xanthan gum is added and is used as carrier, by thallus and bentonite, Xanthan gum stirs evenly, and the bacterium powder that total bacterium amount is 100~50,000,000,000/g is made in 45 DEG C of drying.
9. Mixed Microbes powder according to claim 8, which is characterized in that the carrier is bentonite and xanthan gum according to 5:1 Mass ratio mix.
10. a kind of application of Mixed Microbes powder according to any one of claims 8 as feed addictive, and the application of regulation water quality.
CN201810782000.XA 2018-07-17 2018-07-17 Heterotrophic nitrification-aerobic denitrification bacillus and composite bacterial preparation thereof Active CN108865940B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810782000.XA CN108865940B (en) 2018-07-17 2018-07-17 Heterotrophic nitrification-aerobic denitrification bacillus and composite bacterial preparation thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810782000.XA CN108865940B (en) 2018-07-17 2018-07-17 Heterotrophic nitrification-aerobic denitrification bacillus and composite bacterial preparation thereof

Publications (2)

Publication Number Publication Date
CN108865940A true CN108865940A (en) 2018-11-23
CN108865940B CN108865940B (en) 2021-10-08

Family

ID=64302438

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810782000.XA Active CN108865940B (en) 2018-07-17 2018-07-17 Heterotrophic nitrification-aerobic denitrification bacillus and composite bacterial preparation thereof

Country Status (1)

Country Link
CN (1) CN108865940B (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109943501A (en) * 2019-03-01 2019-06-28 中国水产科学研究院珠江水产研究所 One plant of bacillus megaterium P5-2 and its separation method and application
CN111285723A (en) * 2020-02-26 2020-06-16 江苏思威博生物科技有限公司 Composite auxiliary agent capable of improving survival rate of strains in bio-organic fertilizer and use method thereof
CN112111435A (en) * 2020-10-27 2020-12-22 集美大学 Bacillus NB-1 and culture method and application thereof
CN114657080A (en) * 2020-12-22 2022-06-24 湖北绿天地生物科技有限公司 Binary composite bacterium preparation and application thereof

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2013038216A1 (en) * 2011-09-14 2013-03-21 Szegedi Tudományegyetem Production of biogas from protein-rich resources
CN104164391A (en) * 2014-07-09 2014-11-26 青岛玛斯特生物技术有限公司 Bacillus subtilis and application thereof in aquaculture
CN105060497A (en) * 2015-07-16 2015-11-18 华南理工大学 Compounded oxygen producer for removing nitrite in aquatic water and preparation method
CN105441348A (en) * 2014-09-11 2016-03-30 北京大北农科技集团股份有限公司 New bacillus subtilis strain, microecological preparation and application
CN106244486A (en) * 2016-08-19 2016-12-21 中国海洋大学 The bacillus cereus of one high-efficiency degradation nitrogen pollutant and composite bacteria preparation thereof
JP2018042466A (en) * 2016-09-12 2018-03-22 東洋ゴム工業株式会社 Microorganism culture carrier, sewage treatment method, soil evaluation method, microorganism multiplication performance improving method, and soil improving method

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2013038216A1 (en) * 2011-09-14 2013-03-21 Szegedi Tudományegyetem Production of biogas from protein-rich resources
CN104164391A (en) * 2014-07-09 2014-11-26 青岛玛斯特生物技术有限公司 Bacillus subtilis and application thereof in aquaculture
CN105441348A (en) * 2014-09-11 2016-03-30 北京大北农科技集团股份有限公司 New bacillus subtilis strain, microecological preparation and application
CN105060497A (en) * 2015-07-16 2015-11-18 华南理工大学 Compounded oxygen producer for removing nitrite in aquatic water and preparation method
CN106244486A (en) * 2016-08-19 2016-12-21 中国海洋大学 The bacillus cereus of one high-efficiency degradation nitrogen pollutant and composite bacteria preparation thereof
JP2018042466A (en) * 2016-09-12 2018-03-22 東洋ゴム工業株式会社 Microorganism culture carrier, sewage treatment method, soil evaluation method, microorganism multiplication performance improving method, and soil improving method

Non-Patent Citations (5)

* Cited by examiner, † Cited by third party
Title
曹林 等: ""活性污泥中异养硝化-好氧反硝化菌的分离及其脱氮性能"", 《净水技术》 *
林小涛 等: "《水产动物无公害养殖原理与水环境调控技术 以对虾养殖为实例》", 31 December 2009, 中国环境科学出版社 *
胡咏梅 等: ""枯草芽孢杆菌 Y99-01菌株的净水作用"", 《华中农业大学学报》 *
解玉萌 等: ""两株海水氮降解菌的分离鉴定及其无机氮去除特性初步研究"", 《中国海洋大学学报》 *
赵坤 等: ""凡纳滨对虾养殖池塘高效脱氮芽孢杆菌的分离筛选及特性研究"", 《中国海洋大学学报》 *

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109943501A (en) * 2019-03-01 2019-06-28 中国水产科学研究院珠江水产研究所 One plant of bacillus megaterium P5-2 and its separation method and application
CN109943501B (en) * 2019-03-01 2020-12-01 中国水产科学研究院珠江水产研究所 Bacillus megaterium P5-2 and separation method and application thereof
CN111285723A (en) * 2020-02-26 2020-06-16 江苏思威博生物科技有限公司 Composite auxiliary agent capable of improving survival rate of strains in bio-organic fertilizer and use method thereof
CN112111435A (en) * 2020-10-27 2020-12-22 集美大学 Bacillus NB-1 and culture method and application thereof
CN114657080A (en) * 2020-12-22 2022-06-24 湖北绿天地生物科技有限公司 Binary composite bacterium preparation and application thereof

Also Published As

Publication number Publication date
CN108865940B (en) 2021-10-08

Similar Documents

Publication Publication Date Title
CN101302485B (en) Heterotrophic nitrification microbial preparation, cultivation method and use thereof
CN108865940A (en) One plant of heterotrophic nitrification-aerobic denitrification bacillus and its composite bacteria preparation
CN105861359A (en) Heterotrophic nitrification-aerobic denitrification high temperature resisting strain for producing floc, and application thereof
CN104845920B (en) One plant of ocean Zhuo Beier Salmonella and its application
CN112625942B (en) Aerobic denitrifying bacterium and application thereof
CN104862260B (en) One plant of arthrobacterium and its application with aerobic denitrification ability
CN104911130A (en) Halomonas sp. with denitrogenation capability and application thereof
CN101701197B (en) Novel microorganism flora mixture and mixed nutrient medium thereof
CN108423838B (en) Microbial preparation for ecological safety water system and preparation method thereof
CN111471611B (en) Rhodococcus ruber HDRR1 for purifying inorganic nitrogen and phosphorus in tail water of seawater pond culture and application thereof
CN113913326A (en) Saccharomycopsis oryzae HN05 and application thereof
CN101914464B (en) Alcaligenes sp. MB-N6 for removing nitrite nitrogen pollution out of water and application thereof
CN110104798A (en) A kind of complex microorganism preparations and application for sewage treatment
CN108238681B (en) Composite biological agent for low-temperature sewage treatment and preparation method and application thereof
CN106434408A (en) Citric acid bacillus Y3 with function of degrading brominated flame retardants and application thereof
CN106434424B (en) Vibrios and application thereof with dirty seawater denitrification ability
CN111471612B (en) Rhodococcus ruber HDRR2Y for purifying inorganic nitrogen and phosphorus in seawater pond culture tail water and application thereof
CN115403155A (en) Method for reducing antibiotic resistance genes in pig raising wastewater by utilizing phycobiont technology
CN113025507B (en) Compound microbial agent, preparation thereof and application thereof in deodorization and purification of high-concentration wastewater in livestock and poultry farms
CN110628670B (en) Heterotrophic nitrifying bacteria and application thereof
CN108660087A (en) A kind of complex micro organism fungicide and its preparation method and application for reducing the release of Chicken Manure Compost ammonia
CN108034622B (en) Aerobic denitrifying bacterium ZJ-17 and application thereof
CN108546662A (en) Using the method for nitrifying bacteria community-bacillus Combined Treatment breeding wastewater of immobilization respectively
CN110257303A (en) One plant of ornithine bacillus suitable for handling Shamingdan cyanide wastewater
CN109402029A (en) Isolation and purification method, ammonia nitrogen degradation strain and the application of ammonia nitrogen degradation bacterium

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