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Aerobic denitrification bacterium SLY2-21 applied to denitrifying sewage and application thereof

A technology of aerobic denitrification bacteria and aerobic denitrification, applied in aerobic process treatment, biological water/sewage treatment, microbial-based methods, etc., can solve the problems of limited practical application research and single type of bacteria discovery, To achieve the effect of broad application prospects

Active Publication Date: 2019-05-28
BEIJING UNIV OF CHEM TECH
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

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Problems solved by technology

[0004] So far, the types of bacterial strains have been found to be relatively single, and most of the research has focused on degradation genes and degradation mechanisms, and practical application research is limited.

Method used

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  • Aerobic denitrification bacterium SLY2-21 applied to denitrifying sewage and application thereof
  • Aerobic denitrification bacterium SLY2-21 applied to denitrifying sewage and application thereof
  • Aerobic denitrification bacterium SLY2-21 applied to denitrifying sewage and application thereof

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Experimental program
Comparison scheme
Effect test

Embodiment 1

[0031] The specific steps for the screening of aerobic denitrifying bacteria are as follows:

[0032] 1. Acclimatization and enrichment: Inoculate 10mL of fully mixed fresh landfill leachate into a 250mL Erlenmeyer flask with 100mL LB medium, place on a shaker at 30°C, 150rpm, and cultivate for 48h, and take samples every 12h to qualitatively detect N0 in the medium 3 - -N and NO 2 - -N content. Take 10 mL of the enriched culture medium and transfer it to fresh LB liquid medium, transfer it 5 times, and enrich for 10 days in total.

[0033] Qualitatively detect N0 in the medium with diphenylamine reagent and Gliese reagent at intervals of 12 h 3 - -N and NO 2 - -N content. Use a sterilized dropper to draw 3 drops of culture solution into a sterilized test tube, and then add 3 drops of Griess reagent to the test tube. If the culture solution turns pink or brown, it proves the presence of nitrite. Nitrate reduction positive, the bacteria may be aerobic denitrification b...

Embodiment 2

[0047] Molecular biological identification of aerobic denitrifying bacteria SLY2-21:

[0048] After the above screening and separation, an aerobic denitrification strain SLY2-21 with good denitrification effect was obtained. The strain was Gram-negative, milky white, regular in shape, smooth and moist in surface, and easy to stir up by SEM. The scan found that the SLY2-21 bacteria were rod-shaped, with a size of 1-2um×0.3-0.5um (see figure 1 ).

[0049] 1. Bacterial genomic DNA extraction

[0050] Insert the target strain into LB medium, after culturing overnight, take 1 mL and centrifuge to obtain the bacteria, then use the genome kit to extract the bacterial genome, PCR amplification, agarose gel electrophoresis (1%) verification, and ultraviolet analyzer to check the electrophoresis results .

[0051] 2. PCR amplification of 16SrDNA fragments

[0052] Use universal primers (27f: 5'-AGAGTTTGATCCTGGCTCAG-3', 1492r: 5'-GGTTACCTTGTTACGACTT-3') to carry out PCR reaction, the...

Embodiment 3

[0059] Growth and denitrification characteristics of SLY2-21 strain:

[0060] 1. Inoculate the SLY2-21 strain stored in a refrigerator at 4°C in LB medium at 30°C and 150rpm to expand the culture, use sterile water to prepare a bacterial suspension with an OD of about 1.5, and then inoculate at a 2% inoculation amount Mix well in a 250mL Erlenmeyer flask containing 100mL heterotrophic nitrification medium, and culture at 30°C, 150rpm, on a shaker for 96h. Samples were taken regularly to determine the NH in the supernatant 4 + -N,OD 600 value. In order to reduce the error, three parallel experiments were set up, and the results are shown in image 3 .

[0061] According to the curve, it can be seen that the SLY2-21 bacteria enters the logarithmic phase after 12 hours of growth in the nitrification medium, enters the stable phase after about 27 hours, and enters the decline phase after a short period of stable phase. During strain growth while NH 4 + -N concentration dec...

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Abstract

The invention discloses an aerobic denitrification bacterium SYL2-21 applied to denitrifying sewage and application thereof and belongs to the fields of environmental microorganisms and water treatment biological denitrification. The strain is preserved in China General Microbiological Culture Collection Center (CGMCC) in January 2019, the address is Institute of Microbiology Chinese Academy of Sciences No.3 No.1 yard Beichen west road Chaoyang District Beijing, and a preservation number is CGMCC No.17221. The strain disclosed by the invention is screened and obtained from landfill leachate; the strain disclosed by the invention can effectively remove ammoniacal nitrogen and nitric nitrogen in the sewage; after being enlarged and cultivated, the strain can be directly applied to denitrifying riverway water bodies; the strain has large application potential in actual engineering; from far-reaching significance, the strain has a certain promoting effect on environment protection work.

Description

technical field [0001] The invention relates to the fields of environmental microorganisms and biological denitrification of water treatment, in particular to an aerobic denitrification bacterial strain used for sewage treatment, and simultaneously provides the denitrification efficiency and practical application of the bacterial strain. Background technique [0002] Nitrogen pollution is ubiquitous today, and the forms of nitrogen compounds in water bodies include protein nitrogen, ammonia nitrogen, organic nitrogen, nitrite nitrogen and nitrate nitrogen, so efficient and rapid removal of nitrogen in water is an important topic in the field of water pollution prevention and control. . The theoretical basis of traditional biological denitrification technology is microbial nitrification and denitrification, but there are many defects in traditional biological denitrification technology, which makes the denitrification process discontinuous and inefficient. [0003] The tradi...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): C12N1/20C12N1/02C02F3/02C02F3/34C12R1/025
CPCY02W10/10
Inventor 王晓慧杨静丹刘琳
Owner BEIJING UNIV OF CHEM TECH