Heterotrophic nitrifying and aerobic denitrifying bacterium and culture and application thereof

A technology of aerobic denitrification and heterotrophic nitrification, applied in the field of heterotrophic nitrification and aerobic denitrification bacteria, which can solve the problems of low dissolved oxygen requirements, increased treatment costs, and slow start-up of reactors

Inactive Publication Date: 2013-04-03
TAIYUAN UNIV OF TECH
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  • Abstract
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AI Technical Summary

Problems solved by technology

[0005] First of all, ammonia oxidizing bacteria and nitrous acid oxidizing bacteria are chemoautotrophic bacteria. Due to the long period of time, the reactor starts slowly, which increases the cost of sewage treatment;
[0006] Second, due to the different nutritional requirements and living conditions of nitrifying bacteria and denitrifying bacteria, the entire denitrification process must be carried out in two independent reaction pools of aerobic and anoxic, which increases the volume of the reactor
Or alternate aerobic and anoxic environments in time in the same reactor, but the control of the system is also very cumbersome;
[0007] Third, denitrifying bacteria are heterotrophic bacteria, so the denitrification process requires a high concentration of organic matter. When the BOD: TN in sewage is greater than 2.86, denitrification is normal, but below this value, denitrification cannot be carried out normally.
Some processes use the reflux of nitrifying liquid to solve the problem of insufficient carbon source in the denitrification process, but the reflux of nitrifying liquid is large and the energy consumption is high;
[0008] Fourth, nitrifying bacteria will produce acid during the nitrification process, and acidic conditions can inhibit the nitrification reaction, so alkali needs to be added continuously during the nitrification process, thereby increasing the treatment cost;
[0009] Fifth, the impact resistance is weak, and high concentrations of ammonia nitrogen and nitrite will inhibit nitrification
Compared with autotrophic nitrifying bacteria, although the decomposition efficiency of heterotrophic bacteria is low, they have fast growth rate, high cell yield, low requirements for dissolved oxygen, and strong environmental adaptability. bacteria, so in some environments heterotrophic nitrification is comparable to autotrophic nitrification, or even exceeds autotrophic nitrification

Method used

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  • Heterotrophic nitrifying and aerobic denitrifying bacterium and culture and application thereof
  • Heterotrophic nitrifying and aerobic denitrifying bacterium and culture and application thereof
  • Heterotrophic nitrifying and aerobic denitrifying bacterium and culture and application thereof

Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0069] Embodiment 1: the cultivation of bacterial strain of the present invention

[0070] (1) prepare heterotrophic nitrification medium, subpackage to 250mL Erlenmeyer flask, each bottle subpackage volume is 100mL, 121 ℃ of sterilization 20min; Described heterotrophic nitrification medium is (NH 4 ) 2 SO 4 0.47g, sodium citrate 4.9g, MgSO 4 ·7H 2 O 0.05g, K 2 HPO 4 0.2g, NaCl 0.12g, MnSO 4 4H 2 O 0.01g, FeSO4 0.01g, H 2 O 1000mL, pH 7.0;

[0071] (2) Inoculate the Acinetobacter sp.Y1 stored on the slant of the heterotrophic nitrification medium into a fresh heterotrophic nitrification medium, culture with shaking at 30°C and 120 rpm, and activate the culture for 18 hours for later use.

[0072] (3) The activated bacteria were inoculated into the heterotrophic nitrification medium according to the inoculum amount of 1%, and cultured with constant temperature shaking at 30° C. and 120 rpm.

Embodiment 2

[0073] Embodiment 2: the heterotrophic denitrification performance of bacterial strain of the present invention

[0074] Heterotrophic nitrification medium: (NH 4 ) 2 SO 4 0.47g, sodium citrate 4.9g, MgSO 4 ·7H 2 O 0.05g, K 2 HPO 4 0.2g, NaCl 0.12g, MnSO 4 4H 2 O 0.01g, FeSO4 0.01g, H 2 O 1000 mL, pH 7.0.

[0075] Use heterotrophic nitrification medium, inoculate the activated bacterial suspension at a ratio of 1% (see Example 1 for the method), shake and cultivate under the conditions of 30° C. and 120 rpm, and regularly take samples to detect ammonia nitrogen, hydroxylamine nitrogen, nitrite nitrogen, and nitrate nitrogen and total nitrogen. see results figure 2 . As can be seen from the figure, ammonia nitrogen and total nitrogen are consumed very quickly. In the heterotrophic nitrification medium whose initial ammonia nitrogen concentration is 108.78mg / L, the bacterial strain of the present invention can remove 98.6% of ammonia nitrogen and total nitrogen thro...

Embodiment 3

[0076] Embodiment 3: the aerobic denitrification performance of bacterial strain of the present invention

[0077] Nitrite medium: NaNO 2 0.49g, sodium citrate 6.86g, MgSO 4 ·7H 2 O 0.05g, K 2 HPO 4 0.2g, NaCl 0.12g, MnSO 4 4H 2 O 0.01g, FeSO 4 0.01g, H 2 O 1000mL, pH 7.0,.

[0078] Nitrate medium: NaNO 3 0.61g, sodium citrate 6.86g, MgSO 4 ·7H 2 O 0.05g, K 2 HPO 4 0.2g, NaCl 0.12g, MnSO 4 4H 2 O 0.01g, FeSO 4 0.01g, H 2 O 1000mL, pH 7.0,.

[0079] Use nitrite culture medium and nitrate culture medium, under the condition of initial nitrogen concentration 100mg / L, C / N ratio 20, 1% ratio inoculates the bacterium suspension after the activation (method sees embodiment 1), 30 ℃ , Shaking culture under the condition of 120rpm, take samples regularly to detect the absorbance value, nitrite nitrogen, nitrate nitrogen. see results image 3 and Figure 4 .

[0080] From the data in the figure, it can be seen that the strain Y1 can effectively remove nitrogen when...

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Abstract

The invention relates to a heterotrophic nitrifying and aerobic denitrifying bacterium for efficient denitrification, and the culture and application of the heterotrophic nitrifying and aerobic denitrifying bacterium. The bacterium belongs to an acinetobacter species (Acinetobacter), with the name of Acinetobacter sp.Y1, the preservation registration number of CGMCC NO.6563, the preservation institution of China Microorganism Culture Preservation Management Council General Microbiological Center and the preservation time of September 14th, 2012. The bacterium is separated from activated sludge of coking wastewater, can not only quickly remove ammonia nitrogen, but also grow under the condition that nitrite and nitrate are taken as sole nitrogen sources, and effectively removes nitrite nitrogen and nitrate nitrogen, and can be applied to nitrogen-containing wastewater treatment.

Description

technical field [0001] The invention relates to the field of environmental microorganisms, in particular to a highly efficient denitrification heterotrophic nitrifying aerobic denitrifying bacteria, and its cultivation and application. technical background [0002] Traditional biological denitrification is an organic combination of nitrification and denitrification. The nitrification reaction refers to the NH reaction under aerobic conditions 4 + via NO 2 - Oxidation to NO 3 - process, which was first discovered by Winogradsky in 1890. The traditional nitrification reaction is completed by two kinds of microorganisms, namely ammonia oxidizing bacteria (AOB) (also known as nitrosifying bacteria) and nitrite oxidizing bacteria (NOB) (also known as nitrifying bacteria). [0003] Ammonia oxidizing bacteria and nitrite oxidizing bacteria are both aerobic bacteria that do not require organic carbon sources and are chemoautotrophic bacteria. Generally, the BOD concentration ...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): C12N1/20C02F3/02C02F3/34C12R1/01
CPCY02W10/10
Inventor 刘玉香李风雷刘文静吕永康李亚青叶俊岭宋宇杰
Owner TAIYUAN UNIV OF TECH
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