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Preparation and application of aerobic denitrification bacteria and its agent

A bacterial agent and oxygen removal technology, which is applied in the field of preparation and application of aerobic denitrification bacteria and its bacterial agent, can solve the problems of accumulation and limitation of wide application, and achieve high biomass, high denitrification efficiency, and bacterial agent less effect

Active Publication Date: 2021-12-28
YANTAI INST OF COASTAL ZONE RES CHINESE ACAD OF SCI
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

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Problems solved by technology

However, through the conclusion of the research, it is found that the above-mentioned technologies are all added a large amount of organic carbon sources, only to promote the assimilation of ammonia nitrogen in water to generate organic nitrogen, rather than to remove nitrogen pollutants from water. It is easy to cause the accumulation of ammonia nitrogen and nitrite, which limits the wide application of this technology in the field of water treatment

Method used

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  • Preparation and application of aerobic denitrification bacteria and its agent

Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0042] Acinetobacter YTLJ-N-S10 ( Acinetobacter sp. YTLJ-N-S10) isolation and identification

[0043] 1. Isolation of strains

[0044] The tail water from a seawater fish farming system in the coastal area was used as the stock solution, and was inoculated into a sterilized propagation medium at a 3% inoculum amount. After culturing at 30 °C for 3-7 days, it was diluted and cultured in LB medium, and a single colony was selected. Streak separation was carried out on the agar solid medium to obtain the purified strain YTLJ-N-S10 ( Acinetobacter sp. YTLJ-N-S10).

[0045] 2. Identification of strains

[0046] 2.1. Morphological identification

[0047] The bacterial strain isolated and purified in the above step 1 was analyzed and found to belong to Acinetobacter.

[0048] 2.2 Homology analysis of 16S rDNA sequence

[0049] The colony PCR method was used to amplify the 16S rDNA fragment of the strain obtained in step 1, and the results of amplifying the 16S rRNA gene fra...

Embodiment 2

[0053] Bacillus YTLJ-N-B38 ( Bacillus sp. YTLJ-N-B38) isolation and identification

[0054] 1. Isolation of strains

[0055] Inoculate littoral saltwater prawn feces residues into sterilized propagation medium according to 1% inoculum amount, culture at 35 °C for 5-7 days, then dilute culture in LB medium, and select single colony on agar solid medium Streak separation on the above to obtain the purified strain YTLJ-N-B38 ( Bacillus sp. YTLJ-N-B38).

[0056] 2. Identification of strains

[0057] 2.1. Morphological identification

[0058] The bacterial strain isolated and purified in the above step 1 was analyzed and compared that the bacterial strain belonged to Bacillus.

[0059] 2.2 Homology analysis of 16S rDNA sequence

[0060] The colony PCR method was used to amplify the 16S rDNA fragment of the strain obtained in step 1, and the results of amplifying the 16S rRNA gene fragment and cloning and sequencing showed that the 16S rDNA of the strain had the nucleotide...

Embodiment 3

[0064] Take 500 mL of simulated biogas slurry from livestock and poultry breeding and put it in an Erlenmeyer flask. The ammonia nitrogen concentration of the simulated biogas slurry is 200 mg / L, pH=7.06, C / N ratio is 1, and salinity is 0.2%. The pure Acinetobacter YTLJ-N-S10 bacterial liquid was added to the simulated biogas slurry at a constant temperature of 30 °C for 7 days at a constant temperature of 30 °C. The concentration of ammonia nitrogen dropped to 36 mg / L, and the removal rate reached 82%.

[0065] The pure bacterial liquid of Bacillus YTLJ-N-B38 was added to the high-concentration organic wastewater of simulated food processing according to the inoculation amount of 5%. mg / L, C / N ratio is 50. After 14 days of treatment at a constant temperature of 28°C, the concentrations of COD, ammonia nitrogen, and nitrate nitrogen decreased to 150, 4, and 0.5 mg / L, respectively, and the removal rates reached 92.5%, 90.0%, and 90.0%, respectively.

[0066] Then, the titratio...

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Abstract

The aerobic denitrification strains and bacterial agents thereof of the present invention are obtained by screening new strains of Acinetobacter YTLJ-N-S10 and Bacillus YTLJ-N-B38 respectively pre-cultivated and multiplied, and then vacuum freeze-dried to obtain corresponding single bacteria Bacteria powder is prepared by mixing the powder of single bacteria, and then mixing it with the crude exopolysaccharide of aerobic denitrification bacteria and auxiliary materials. The Acinetobacter YTLJ-N-S10 and Bacillus YTLJ-N-B38 are preserved in the Guangdong Microbial Culture Collection Center, and the preservation numbers are GDMCC No: 61690 and GDMCC No: 61774, respectively. The strain and its agent can strengthen the heterotrophic nitrification and aerobic denitrification of water bodies, and at the same time have the effect of inhibiting pathogenic bacteria, and can be used for purifying various sewage and strengthening the removal of nitrogen pollutants.

Description

technical field [0001] The invention relates to the technical field of environmental protection, in particular to the preparation and application of an aerobic denitrification bacterial strain and its bacterial agent. Background technique [0002] Factory farming is an important way of modern fish farming. The large-scale discharge of aquaculture wastewater has a great impact on the water quality of offshore aquaculture waters. The water environment pollution and frequent aquatic diseases caused by large-scale industrial aquaculture have seriously plagued and hindered the development of my country's aquaculture industry. The in-situ purification treatment technology of aquaculture water has the advantages of less damage to the ecological environment and less tail water discharge. It can not only protect the offshore ecological environment, but also obtain high-yield and high-quality aquatic products. Therefore, in-situ purification of aquaculture water is one of the key dev...

Claims

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Application Information

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Patent Type & Authority Patents(China)
IPC IPC(8): C12N1/20C02F3/34C02F3/02C12R1/07C12R1/01C02F101/30
CPCC12N1/20C02F3/341C02F3/02C02F2101/30Y02W10/10
Inventor 吕剑武君王建华张翠
Owner YANTAI INST OF COASTAL ZONE RES CHINESE ACAD OF SCI