CN107058207A - A kind of rejuvenation method of the heterotrophic nitrification aerobic denitrifying bacterium for bisphenols nitric wastewater of degrading - Google Patents
A kind of rejuvenation method of the heterotrophic nitrification aerobic denitrifying bacterium for bisphenols nitric wastewater of degrading Download PDFInfo
- Publication number
- CN107058207A CN107058207A CN201710251089.2A CN201710251089A CN107058207A CN 107058207 A CN107058207 A CN 107058207A CN 201710251089 A CN201710251089 A CN 201710251089A CN 107058207 A CN107058207 A CN 107058207A
- Authority
- CN
- China
- Prior art keywords
- bisphenols
- culture
- fluid nutrient
- water distribution
- rejuvenation
- 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.)
- Withdrawn
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N1/00—Microorganisms, 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
- C12N1/36—Adaptation or attenuation of cells
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N1/00—Microorganisms, 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
- C12N1/20—Bacteria; Culture media therefor
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/34—Organic compounds containing oxygen
- C02F2101/345—Phenols
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Health & Medical Sciences (AREA)
- Organic Chemistry (AREA)
- Microbiology (AREA)
- Biotechnology (AREA)
- Zoology (AREA)
- Bioinformatics & Cheminformatics (AREA)
- Wood Science & Technology (AREA)
- Genetics & Genomics (AREA)
- Tropical Medicine & Parasitology (AREA)
- Biomedical Technology (AREA)
- Virology (AREA)
- Biochemistry (AREA)
- General Engineering & Computer Science (AREA)
- General Health & Medical Sciences (AREA)
- Medicinal Chemistry (AREA)
- Cell Biology (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)
Abstract
The invention belongs to technical field of environmental microorganism, it is related to the rejuvenation of bacterial strain, is related specifically to a kind of rejuvenation method for the heterotrophic nitrification aerobic denitrifying bacterium for handling bisphenols nitric wastewater.Cultivated using the culture medium containing common carbon source, it is gradually added into the nitrogenous water distribution of bisphenols and improves its proportioning, so that microorganism is by an incremental domestication process and gradually recovers its adaptability to bis-phenol pollutant, the heterotrophic nitrification aerobic denitrifying bacterial strain using bis-phenol pollutant as carbon source is finally obtained.This method cultivates the method for carrying out rejuvenation relative to the direct culture medium with containing common carbon source or the nitrogenous water distribution of bisphenols repeatedly, and rejuvenation has higher success rate, and this method is operationally simple and easy to apply, time-consuming less.And the degraded situation by the use of bis-phenol pollutant, ammonia nitrogen removal frank and its conversion ratio of gaseous nitrogen etc. is converted into as the index for evaluating rejuvenation bacterial strain performance, it is relatively comprehensive.
Description
Technical field
The invention belongs to field of environment microorganism, it is related to the rejuvenation of bacterial strain, is related specifically to a kind of processing bisphenols and contains
The rejuvenation method of the heterotrophic nitrification aerobic denitrifying bacterium of nitrogen sewage.
Background technology
Traditional ammonia-nitrogen sewage processing needs the nitrification by autotrophy and two stages ability of denitrification of heterotrophism
It can complete.Because the growth rate of Autotrophic nitrification bacterium causes nitrification efficiency relatively low slowly, so as to considerably increase processing procedure
Time-consuming, the stability of whole sewage disposal process denitrification effect is also easily affected.And the nitrification and denitrification stage needs
Separately carry out adding energy consumption, while floor space is larger, investment and operating cost are larger.
The discovery and application of heterotrophic nitrification aerobic denitrifying bacteria largely solve above mentioned problem so that aerobic
Under the conditions of nitrification and denitrification be possibly realized in same reactor.It is different when dirty organic pollutants have more
Type bacterium is supported because comparatively fast, so as to easily become dominant bacteria, particularly many heterotrophic nitrifications are good using organic matter multiplication rate
Oxygen denitrifying bacteria can be carbon source using hardly degraded organic substance, and this goes for dirty Organic substance in water particularly hardly degraded organic substance
Except with denitrogenation important in inhibiting.
Usual heterotrophic nitrification aerobic denitrifying bacterium passes through the Effec-tive Function of certain time, occurs specific due to iterating
Activity is degenerated, or function reduction phenomenon occurs, it is necessary to rejuvenation be carried out to it, to maintain its denitrogenation because culture presevation is improper
The stability of energy.The method that existing rejuvenation of spawn technology is typically cultivated repeatedly using bacterium culture medium, but it is generally multiple
Strengthen less effective and time-consuming longer.Therefore propose that the efficient rejuvenation method of heterotrophic nitrification aerobic denitrifying bacterium has important meaning
Justice.The invention provides a kind of rejuvenation side of good, the quick and simple and easy to apply heterotrophic nitrification aerobic denitrifying bacterium of effect of rejuvenation
Method.
The content of the invention
For deficiency present in existing rejuvenation technique, it is an object of the invention to provide one kind degraded nitrogenous dirt of bisphenols
The rejuvenation method of the heterotrophic nitrification aerobic denitrifying bacterium of water, to provide lasting microorganism for the processing of bisphenols nitric wastewater
Source.
Technical scheme:
A kind of rejuvenation method of the heterotrophic nitrification aerobic denitrifying bacterium for bisphenols nitric wastewater of degrading, step is as follows:
(1) domestication culture is carried out to the strain for needing rejuvenation:
(1.1) fluid nutrient medium I is prepared, the concentration proportioning of various materials is:(NH4)2SO40.1-0.5g/L, citric acid
Sodium 1-3g/L, sodium acetate 1-3g/L, K2HPO4·2H2O 5-6g/L、KH2PO4 2-3g/L、MgSO4·7H2O 0.2-0.8g/L、
CaCl20.02-0.1g/L, pH are adjusted to 6.8-7.2;
(1.2) the nitrogenous water distribution of bisphenols is prepared, the concentration proportioning of various materials is:(NH4)2SO4It is 0.01-0.02g/L, double
Aldehydes matter 0.2-0.5g/L, K2HPO4·2H2O 5-6g/L、KH2PO4 2-3g/L、MgSO4·7H2O0.2-0.8g/L、CaCl2
0.02-0.1g/L, pH are adjusted to 6.8-7.2;
The nitrogenous water distribution of the fluid nutrient medium I and bisphenols of preparation is subjected to sterilization treatment;
(1.3) three class I liquid I culture mediums are aseptically prepared:
The first kind is the fluid nutrient medium I of 100% volume;
Equations of The Second Kind includes multiple fluid nutrient mediums, each nitrogenous by the fluid nutrient medium I and bisphenols of different volumes ratio
Water distribution is made into, and the volume ratio shared by fluid nutrient medium I is prepared by the order successively decreased, fluid nutrient medium I volume ratio
Scope is 90%~10%;Volume ratio shared by the nitrogenous water distribution of bisphenols is prepared by incremental order, the nitrogenous water distribution of bisphenols
Volume ratio scope be 10%~90%;
3rd class is the nitrogenous water distribution of bisphenols of 100% volume;
The three class I liquid I culture mediums prepared are subjected to sterilization treatment;
(1.4) strain for needing rejuvenation is carried out into progressively domestication to cultivate, first by first kind fluid nutrient medium, domestication training
Support 1-2d;The incremental order of volume ratio again as shared by the nitrogenous water distribution of bisphenols in matched somebody with somebody fluid nutrient medium changes Equations of The Second Kind liquid
Body culture medium, often changes once domestication culture 1-2d;Finally change the 3rd class I liquid I culture medium, domestication culture 1-2d;
What domestication was cultivated concretely comprises the following steps:Aseptically, the heterotrophism of rejuvenation will be needed with phosphate buffer first
Nitrification aerobic denitrification strain is cleaned and centrifuged 2-3 times, removes supernatant, is subsequently added into phosphate buffer and is carried out concussion weight
It is outstanding, uniform bacterium solution is obtained, bacterium solution is pipetted and is seeded in the fluid nutrient medium of step (1.3) preparation so that the concentration of initial strain
For OD600=0.1-0.15, finally by fluid nutrient medium be placed in it is sterile, 30-35 DEG C, tamed under conditions of 100-150rpm
Culture;Wherein, the concentration proportioning of each material is in phosphate buffer:K2HPO4·2H2O 5-6g/L、KH2PO42-3g/L, will
Phosphate buffer pH is adjusted to 6.8-7.2;Centrifugal condition is:8000-10000×g、5min、4℃;OD600For in 600nm ripples
The bacterial concentration measured under length;
(2) bacterium after domestication culture is isolated and purified:
Solid medium is prepared, the concentration proportioning of various materials is:(NH4)2SO40.1-0.5g/L, sodium citrate 1-3g/
L, sodium acetate 1-3g/L, K2HPO4·2H2O 5-6g/L、KH2PO4 2-3g/L、MgSO4·7H2O0.2-0.8g/L、CaCl2
0.02-0.1g/L, agar 20g/L, pH are adjusted to 6.8-7.2;
The microbionation after culture will be tamed with plate streak to the solid medium that sterilizes, flat board is inverted in 30-35
Culture 2-3d is to obtain single bacterium colony in DEG C constant incubator;
(3) primary dcreening operation is carried out to efficient bacterium:
A. the single bacterium colony in picking flat board is seeded in first kind fluid nutrient medium respectively, by the first kind liquid after inoculation
Body culture medium is placed in 30-35 DEG C, isothermal vibration culture 1-2d under the conditions of 100-150rpm, and ammonia nitrogen is measured by sampling and total nitrogen is removed
Rate;
B. ammonia nitrogen and total nitrogen removal level to measure reaches the bacterial strain of the normal removal level more than 80% of strain, with OD600
It is seeded to respectively in the 3rd class I liquid I culture medium for 0.1-0.15 inoculum concentration, the 3rd class I liquid I culture medium after inoculation is placed in
30-35 DEG C, isothermal vibration culture 2-3d under the conditions of 100-150rpm, are measured by sampling bis-phenol pollutant, ammonia nitrogen and total nitrogen and remove
Rate;
Repeat step B, until the bis-phenol pollutant, ammonia nitrogen and total nitrogen of measure remove the normal removal level before degeneration that reaches
And keep stable.
(4) nitrogen balance analysis is carried out to efficient bacterium.By the bacterial strain obtained in step (3) with OD600For connecing for 0.1-0.15
The amount of kind is seeded in the nitrogenous water distribution of bisphenols, and the gaseous mixture (volume ratio 3/7) that access is made up of oxygen and helium is aerated,
Reaction system is subjected to encapsulation process after 10-20min to be aerated, the static gas wave refrigerator 2-3d in 30-35 DEG C of incubator.Produce
Gas is determined with gas chromatography (GC), obtains N2And N2O concentration;Determine liquid portion total nitrogen, ammonia nitrogen, nitrate nitrogen and nitrous
The concentration of state nitrogen, pellet fraction is handled with freeze-drying, the concentration of organic nitrogen in somatic cells is determined, by determining nitrogen
Amount, which is calculated, determines that bacterial strain, to the metabolic characteristic of ammonia nitrogen, obtains the heterotrophic nitrification aerobic denitrifying of efficient degradation bisphenols nitric wastewater
Bacterial strain.
The effect and benefit of the present invention:The invention provides a kind of efficient, simple and easy to apply heterotrophic nitrification aerobic denitrifying
The rejuvenation method of bacterium.Cultivated using the culture medium containing common carbon source, be gradually added into the nitrogenous water distribution of bisphenols and improve it and match somebody with somebody
Than so that microorganism is by an incremental domestication process and gradually recovers its adaptability to bis-phenol pollutant,
Finally obtain the heterotrophic nitrification aerobic denitrifying bacterial strain using bis-phenol pollutant as carbon source.This method is relative to directly with containing common
The method for carrying out rejuvenation is cultivated in the nitrogenous water distribution of culture medium or bisphenols of carbon source repeatedly, and rejuvenation has higher success rate, and in behaviour
It is simple and easy to apply on work, take less.And using the degraded situation of bis-phenol pollutant, ammonia nitrogen removal frank and its it is converted into gaseous state
Conversion ratio of nitrogen etc. is relatively more comprehensive as the index for evaluating rejuvenation bacterial strain performance.
Embodiment
Normal HS-2 strains are that the heterotrophic nitrification aerobic denitrifying with the nitrogenous water distribution function of efficient degradation Bisphenol F is thin
Bacterium, the HS-2 bacterial strains that present embodiment has been degenerated to function carry out rejuvenation, and step is as follows:
(1) domestication culture is carried out to the HS-2 strains for needing rejuvenation:
(1.1) fluid nutrient medium I is prepared, the concentration proportioning of various materials is:(NH4)2SO40.3g/L, sodium citrate 2g/
L, sodium acetate 2g/L, K2HPO4·2H2O 5.5g/L、KH2PO4 2.6g/L、MgSO4·7H2O0.2g/L、CaCl20.02g/L,
PH is adjusted to 7.0;
(1.2) the nitrogenous water distribution of Bisphenol F is prepared, the concentration proportioning of various materials is:(NH4)2SO40.012g/L, Bisphenol F
0.3g/L、K2HPO4·2H2O 5.5g/L、KH2PO4 2.6g/L、MgSO4·7H2O 0.2g/L、CaCl20.02g/L, pH are adjusted
To 7.0;
The nitrogenous water distribution of the fluid nutrient medium I and Bisphenol F of preparation is subjected to sterilization treatment;
(1.3) three class I liquid I culture mediums are aseptically prepared:
The first kind is the fluid nutrient medium I of 100% volume;
Equations of The Second Kind includes multiple fluid nutrient mediums, each nitrogenous is matched somebody with somebody by the fluid nutrient medium I and Bisphenol F of different volumes ratio
Water is made into, and the volume ratio shared by fluid nutrient medium I is prepared by the order successively decreased, fluid nutrient medium I volume ratio model
Enclose for 80%, 60%, 40%, 20%;Volume ratio shared by the nitrogenous water distribution of Bisphenol F is prepared by incremental order, and Bisphenol F is nitrogenous
The volume ratio scope of water distribution is 20%, 40%, 60%, 80%;
3rd class is the nitrogenous water distribution of Bisphenol F of 100% volume;
The three class I liquid I culture mediums prepared are subjected to sterilization treatment;
(1.4) strain for needing rejuvenation is carried out into progressively domestication to cultivate, first by first kind fluid nutrient medium, domestication training
Support 1d;Again by the culture medium of the fluid nutrient medium I of 80% volume and the nitrogenous water distribution composition of the sterilizing Bisphenol F of 20% volume, 60%
The culture medium of the fluid nutrient medium I of volume and the nitrogenous water distribution composition of the sterilizing Bisphenol F of 40% volume, the Liquid Culture of 40% volume
Culture medium, the fluid nutrient medium I of 20% volume and 80% volume of the nitrogenous water distribution composition of sterilizing Bisphenol F of base I and 60% volume
The order of culture medium of sterilizing Bisphenol F nitrogenous water distribution composition change Equations of The Second Kind fluid nutrient medium, often change once domestication culture
1d;Finally change the 3rd class I liquid I culture medium, domestication culture 1d;
What domestication was cultivated concretely comprises the following steps:Aseptically, the heterotrophism of rejuvenation will be needed with phosphate buffer first
Nitrification aerobic denitrification strain is cleaned and centrifuged 2 times, removes supernatant, is subsequently added into phosphate buffer and is carried out concussion resuspension,
Uniform bacterium solution is obtained, bacterium solution is pipetted and is seeded in the fluid nutrient medium of step (1.3) preparation so that initially the concentration of strain is
OD600=0.1, finally by fluid nutrient medium be placed in it is sterile, 35 DEG C, domestication culture is carried out under conditions of 150rpm;Wherein, phosphoric acid
The concentration proportioning of each material is in salt buffer:K2HPO4·2H2O 5.5g/L、KH2PO42.6g/L, by phosphate buffer pH
Adjust to 7.0;Centrifugal condition is:10000×g、5min、4℃;OD600For the bacterial concentration measured under 600nm wavelength;
(2) bacterium after domestication culture is isolated and purified:
Solid medium is prepared, the concentration proportioning of various materials is:(NH4)2SO40.3g/L, sodium citrate 2g/L, acetic acid
Sodium 2g/L, K2HPO4·2H2O 5.5g/L、KH2PO4 2.6g/L、MgSO4·7H2O 0.2g/L、CaCl20.02g/L, agar
20g/L, pH are adjusted to 7.0;
The microbionation after culture will be tamed with plate streak to the solid medium that sterilizes, flat board is inverted in 35 DEG C of perseverances
2d is cultivated in warm incubator to obtain single bacterium colony;
(3) primary dcreening operation is carried out to efficient bacterium:
A. totally 12 single bacterium colonies are seeded in the first kind fluid nutrient medium HAW1-12 in picking flat board respectively, will be inoculated with
First kind fluid nutrient medium afterwards is placed in 35 DEG C, isothermal vibration culture 1d under the conditions of 150rpm, and ammonia nitrogen is measured by sampling and total nitrogen is gone
Except rate;
B. ammonia nitrogen and total nitrogen removal level to measure reach strain normally the bacterial strain HAW2-4 of removal level more than 80%,
HAW6, HAW8-10, with OD600It is seeded to respectively in the 3rd class I liquid I culture medium for 0.1 inoculum concentration, by the 3rd class after inoculation
Fluid nutrient medium is placed in 35 DEG C, isothermal vibration culture 2d under the conditions of 150rpm, and Bisphenol F, ammonia nitrogen and nitrogen removal rate is measured by sampling;
Repeat step B, respectively reaches 99%, 96% and 90% and protects until filtering out Bisphenol F, ammonia nitrogen and nitrogen removal rate
Two bacterial strains HAW3, HAW6 for keeping steady fixed.
(4) nitrogen balance analysis is carried out to efficient bacterium.By the bacterial strain HAW3 and HAW6 that are obtained in step (3) respectively with OD600
It is seeded to for 0.1 inoculum concentration in the nitrogenous water distribution of Bisphenol F, and accesses the gaseous mixture (volume ratio 3/7) being made up of oxygen and helium
It is aerated, reaction system is subjected to encapsulation process after 10min to be aerated, the static gas wave refrigerator 2d in 35 DEG C of incubators.Produce
Gas with gas chromatography (GC) determine, obtain N2And N2O concentration;Determine liquid portion total nitrogen, ammonia nitrogen, nitrate nitrogen and Asia
The concentration of nitrate nitrogen, pellet fraction is handled with freeze-drying, the concentration of organic nitrogen in somatic cells is determined, by nitrogen
Quantitative to calculate the metabolic characteristic for determining bacterial strain to ammonia nitrogen, more than 47% initial ammonia nitrogen can be converted into by obtained bacterial strain HAW6
N2, it is same with normal strains function phase before degeneration.
Claims (1)
1. a kind of rejuvenation method of the heterotrophic nitrification aerobic denitrifying bacterium for bisphenols nitric wastewater of degrading, it is characterised in that step
It is as follows:
(1) domestication culture is carried out to the strain for needing rejuvenation:
(1.1) fluid nutrient medium I is prepared, the concentration proportioning of various materials is:(NH4)2SO40.1-0.5g/L, sodium citrate 1-
3g/L, sodium acetate 1-3g/L, K2HPO4·2H2O 5-6g/L、KH2PO4 2-3g/L、MgSO4·7H2O 0.2-0.8g/L、CaCl2
0.02-0.1g/L, pH are adjusted to 6.8-7.2;
(1.2) the nitrogenous water distribution of bisphenols is prepared, the concentration proportioning of various materials is:(NH4)2SO40.01-0.02g/L, bisphenols
Material 0.2-0.5g/L, K2HPO4·2H2O 5-6g/L、KH2PO4 2-3g/L、MgSO4·7H2O 0.2-0.8g/L、CaCl2
0.02-0.1g/L, pH are adjusted to 6.8-7.2;
The nitrogenous water distribution of the fluid nutrient medium I and bisphenols of preparation is subjected to sterilization treatment;
(1.3) three class I liquid I culture mediums are aseptically prepared:
The first kind is the fluid nutrient medium I of 100% volume;
Equations of The Second Kind includes multiple fluid nutrient mediums, each by the nitrogenous water distribution of fluid nutrient medium I and bisphenols of different volumes ratio
It is made into, and the volume ratio shared by fluid nutrient medium I is prepared by the order successively decreased, fluid nutrient medium I volume ratio scope
For 90%~10%;Volume ratio shared by the nitrogenous water distribution of bisphenols is prepared by incremental order, the body of the nitrogenous water distribution of bisphenols
Product proportion is 10%~90%;
3rd class is the nitrogenous water distribution of bisphenols of 100% volume;
The three class I liquid I culture mediums prepared are subjected to sterilization treatment;
(1.4) the heterotrophic nitrification aerobic denitrifying strain for needing rejuvenation is carried out into progressively domestication to cultivate, first by first kind liquid
Body culture medium, domestication culture 1-2d;Change again in Equations of The Second Kind fluid nutrient medium, the second class I liquid I is accounted for from the nitrogenous water distribution of bisphenols
The 10% of the volume of culture medium starts, and gradually increases the volume ratio of the nitrogenous water distribution of bisphenols, until the nitrogenous water distribution of bisphenols is accounted for
The 90% of the volume of Equations of The Second Kind fluid nutrient medium, often increases once, domestication culture 1-2d;Finally change the 3rd class I liquid I culture
Base, domestication culture 1-2d;
Tame the specific steps of culture:Aseptically, it is with phosphate buffer that the heterotrophic nitrification for needing rejuvenation is good first
Oxygen denitrification strain is cleaned and centrifuged 2-3 times, removes supernatant;It is subsequently added into phosphate buffer and carries out concussion resuspension, obtains
Uniform bacterium solution, pipettes bacterium solution and is seeded in the fluid nutrient medium of step (1.3) preparation so that the concentration of initial strain is OD600=
0.1-0.15, finally by fluid nutrient medium be placed in it is sterile, 30-35 DEG C, domestication culture is carried out under conditions of 100-150rpm;Its
In, the concentration proportioning of each material is in phosphate buffer:K2HPO4·2H2O 5-6g/L、KH2PO42-3g/L, by phosphate
PH of buffer is adjusted to 6.8-7.2;Centrifugal condition is:8000-10000×g、5min、4℃;OD600To be surveyed under 600nm wavelength
The heterotrophic nitrification aerobic denitrifying bacterium bacteria concentration obtained;
(2) bacterium after domestication culture is isolated and purified:
Solid medium is prepared, the concentration proportioning of various materials is:(NH4)2SO40.1-0.5g/L, sodium citrate 1-3g/L, second
Sour sodium 1-3g/L, K2HPO4·2H2O 5-6g/L、KH2PO4 2-3g/L、MgSO4·7H2O 0.2-0.8g/L、CaCl2 0.02-
0.1g/L, agar 20g/L, pH are adjusted to 6.8-7.2;
The heterotrophic nitrification aerobic denitrifying bacterium tamed after culture is seeded to sterilizing solid medium with plate streak, by flat board
It is inverted in 30-35 DEG C of constant incubator and cultivates 2-3d to obtain single bacterium colony;
(3) primary dcreening operation is carried out to efficient bacterium:
A. the single bacterium colony in picking flat board is seeded in first kind fluid nutrient medium respectively, and the first class I liquid I after inoculation is trained
Foster base is placed in 30-35 DEG C, isothermal vibration culture 1-2d under the conditions of 100-150rpm, and ammonia nitrogen and nitrogen removal rate is measured by sampling;
B. ammonia nitrogen and nitrogen removal rate level to measure reaches the bacterial strain of the normal removal level more than 80% of strain, with OD600For
0.1-0.15 inoculum concentration is seeded in the 3rd class I liquid I culture medium respectively, and the 3rd class I liquid I culture medium after inoculation is placed in
30-35 DEG C, isothermal vibration culture 2-3d under the conditions of 100-150rpm, are measured by sampling bis-phenol pollutant, ammonia nitrogen and total nitrogen and remove
Rate;
Repeat step B, until bis-phenol pollutant, ammonia nitrogen and the total nitrogen removal of measure reach the preceding normal removal level of degeneration and protect
It is fixed to keep steady;
(4) nitrogen balance analysis is carried out to efficient bacterium:By the bacterial strain obtained in step (3) with OD600For 0.1-0.15 inoculum concentration
It is seeded in the nitrogenous water distribution of bisphenols, and accesses oxygen and helium volume ratio 3:The gaseous mixture of 7 compositions is aerated, and waits to be aerated
Reaction system is subjected to encapsulation process after 10-20min, the static gas wave refrigerator 2-3d in 30-35 DEG C of incubator;The gas of generation is used
Gas chromatography is determined, and obtains N2And N2O concentration;The concentration of liquid portion total nitrogen, ammonia nitrogen, nitrate nitrogen and nitrite nitrogen is determined,
Pellet fraction is handled with freeze-drying, the concentration of organic nitrogen in somatic cells is determined, is determined by the quantitative calculating to nitrogen
Bacterial strain obtains the heterotrophic nitrification aerobic denitrifying bacterial strain of efficient degradation bisphenols nitric wastewater to the metabolic characteristic of ammonia nitrogen.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710251089.2A CN107058207A (en) | 2017-04-19 | 2017-04-19 | A kind of rejuvenation method of the heterotrophic nitrification aerobic denitrifying bacterium for bisphenols nitric wastewater of degrading |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710251089.2A CN107058207A (en) | 2017-04-19 | 2017-04-19 | A kind of rejuvenation method of the heterotrophic nitrification aerobic denitrifying bacterium for bisphenols nitric wastewater of degrading |
Publications (1)
Publication Number | Publication Date |
---|---|
CN107058207A true CN107058207A (en) | 2017-08-18 |
Family
ID=59600205
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201710251089.2A Withdrawn CN107058207A (en) | 2017-04-19 | 2017-04-19 | A kind of rejuvenation method of the heterotrophic nitrification aerobic denitrifying bacterium for bisphenols nitric wastewater of degrading |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN107058207A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109082399A (en) * | 2018-09-14 | 2018-12-25 | 东北农业大学 | A kind of rejuvenation method for the high-temperature micro-aerobic compost keeping nitrogen bacterium reducing livestock excrement composting ammonia volatilization |
CN111647539A (en) * | 2020-07-06 | 2020-09-11 | 重庆工商大学 | Method for strengthening film forming capability of aerobic denitrifying bacteria |
CN113774092A (en) * | 2021-09-27 | 2021-12-10 | 哈尔滨工业大学(深圳) | Method for synthesizing isoprene from environmental wastewater |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102633369A (en) * | 2012-04-17 | 2012-08-15 | 西安建筑科技大学 | Method for repairing micro-polluted water body by utilizing bottom mud biological agent |
CN104673738A (en) * | 2015-02-13 | 2015-06-03 | 中蓝连海设计研究院 | Acclimatization and screening method for heterotrophic nitrification aerobic denitrifying bacteria |
-
2017
- 2017-04-19 CN CN201710251089.2A patent/CN107058207A/en not_active Withdrawn
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102633369A (en) * | 2012-04-17 | 2012-08-15 | 西安建筑科技大学 | Method for repairing micro-polluted water body by utilizing bottom mud biological agent |
CN104673738A (en) * | 2015-02-13 | 2015-06-03 | 中蓝连海设计研究院 | Acclimatization and screening method for heterotrophic nitrification aerobic denitrifying bacteria |
Non-Patent Citations (4)
Title |
---|
LU HONG等: "Simultaneous bisphenol F degradation,heterotrophic nitrification and aerobic denitrification by a bacterial consortium", 《J. CHEM. TECHNOL. BIOTECHNOL.》 * |
于景芝主编: "《酵母生产与应用手册》", 31 July 2005 * |
李双石主编: "《微生物实用技能训练》", 31 August 2014 * |
褚志义主编: "《生物合成药物学》", 31 May 1991 * |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109082399A (en) * | 2018-09-14 | 2018-12-25 | 东北农业大学 | A kind of rejuvenation method for the high-temperature micro-aerobic compost keeping nitrogen bacterium reducing livestock excrement composting ammonia volatilization |
CN109082399B (en) * | 2018-09-14 | 2022-08-09 | 东北农业大学 | Rejuvenation method of high-temperature micro-aerobic composting nitrogen-retaining bacteria for reducing ammonia volatilization of livestock and poultry manure compost |
CN111647539A (en) * | 2020-07-06 | 2020-09-11 | 重庆工商大学 | Method for strengthening film forming capability of aerobic denitrifying bacteria |
CN111647539B (en) * | 2020-07-06 | 2022-07-08 | 重庆工商大学 | Method for strengthening film forming capability of aerobic denitrifying bacteria |
CN113774092A (en) * | 2021-09-27 | 2021-12-10 | 哈尔滨工业大学(深圳) | Method for synthesizing isoprene from environmental wastewater |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN105036853B (en) | A kind of method that biological organic fertilizer is prepared using chicken manure fermenting | |
CN103275891B (en) | Endophyte and application thereof | |
CN104862257B (en) | A kind of method of indigenous nitrogen microbial enrichment culture and its application in ammonia nitrogen pollution in water body improvement | |
Yanai et al. | Fungal N2O production in an arable peat soil in Central Kalimantan, Indonesia | |
CN102391961B (en) | Raoultella ornithinolytica N-4 bacterial strains and preparation and application thereof | |
CN102373161B (en) | Bacterium for reducing mercury pollution in seawater and application thereof | |
CN103627658B (en) | Microbial remediation agent for remediating soil ecosystem | |
Oishi et al. | Growth of ammonia-oxidizing archaea and bacteria in cattle manure compost under various temperatures and ammonia concentrations | |
CN102815792A (en) | Microbe-enzyme composite preparation used for restoring water in urban and rural polluted river, and its preparation method | |
CN110387339B (en) | Ochrobactrum intermedium B522 and application thereof | |
CN103374525B (en) | Wastewater treating microbial agent and preparation method thereof | |
CN107058207A (en) | A kind of rejuvenation method of the heterotrophic nitrification aerobic denitrifying bacterium for bisphenols nitric wastewater of degrading | |
CN106676022A (en) | Method for preparing microbe bacteria liquid for treating black-odor riverway | |
CN102433278B (en) | Enrichment culture method of homoacetogenic bacteria | |
CN103103153A (en) | Anaerobic denitrification phosphorus-accumulating bacteria strain with denitrification and phosphorous removal effects and application thereof | |
CN102250783B (en) | Enrichment culturing method for ammonia oxidizing bacteria | |
CN107858305B (en) | Bacterium for efficiently degrading tetracycline and application thereof | |
NO20082062L (en) | Process for cultivation of microorganisms | |
CN104152373B (en) | Bacterial strain capable of efficiently degrading pendimethalin and application thereof | |
CN103305443A (en) | Preparation and method for restoring ammonia nitrogen-containing industrial sewage | |
CN108421402A (en) | A kind of production method of charcoal base biology composite deodurizing material | |
CN107828692A (en) | One plant of pottery Salmonella in distress and its microbial bacterial agent preparation and application | |
CN103865853B (en) | One strain quinclorac efficient degrading bacteria and uses thereof and using method | |
KR102206153B1 (en) | Novel Azospira sp. Bacterium and method for reducing nitrous oxide using the same | |
CN103820372B (en) | One strain quinclorac efficient degrading bacteria and uses thereof and using method |
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 | ||
WW01 | Invention patent application withdrawn after publication |
Application publication date: 20170818 |
|
WW01 | Invention patent application withdrawn after publication |