Acinetobacter baumannii AL-6 and application thereof
A technology of Acinetobacter baumannii and bacterial liquid, applied in the direction of bacteria, biological water/sewage treatment, microorganisms, etc., can solve the complex process of biological removal of ammonia nitrogen, the limited selection of heterotrophic nitrification-aerobic denitrification strains, etc. problem, to achieve good ammonia nitrogen removal effect, reduce operation and maintenance costs, and improve treatment efficiency
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Embodiment 1
[0032] Embodiment 1: Isolation and identification of bacteria
[0033] 1. Isolation and purification of bacteria
[0034] The Acinetobacter baumannii AL-6 of the present invention is isolated from the activated sludge in the aeration tank of the Chongqing Jiguanshi Sewage Plant, and is obtained through repeated alternation of acclimatization and cultivation of liquid medium and scribing and screening of solid medium plate. The specific implementation steps are as follows:
[0035] 1) Pipette 1 mL of mud-water mixture from the sewage plant into 80 mL of ammonia-nitrogen liquid medium, and acclimatize at constant temperature for 72 h at 120 rpm and 30 °C. Take 1 mL of the cultured bacterial liquid and transfer it to 80 mL of ammonia nitrogen liquid medium for the second acclimatization culture, which lasts for 48 h.
[0036] 2) Dilute the enriched and acclimatized bacterial solution, and the dilution factor is 10 -1 -10 -6 , spread the diluted bacterial solution on a plate c...
Embodiment 2
[0047] Implementation 2: Removal Ability of Acinetobacter baumannii AL-6 to Ammonia Nitrogen and Total Nitrogen in Wastewater with Different Ammonia Nitrogen Concentrations
[0048] Take NH 4 + -N is nitrogen source, CH 3 COONa is the carbon source, and NH in wastewater 4 + -N concentrations of 80 mg / L, 140 mg / L and 210 mg / L were used to investigate the growth of strain AL-6 and the removal ability of ammonia nitrogen and total nitrogen. Wastewater initial NH 4 + The -N concentration is 80 mg / L, the C / N is 10, the pH is controlled at 7~8, and cultured in a shaker at 30°C and 120 rpm. At 30 h, strain OD 600 increased to 1.2, at this time the TN removal rate reached 90.8%, and the NH 4 + The -N removal rate reached 99.9%, the intermediate product nitrate accumulation was 9.9 mg / L, and the nitrite accumulation was 0.1 mg / L. Wastewater initial NH 4 + -N concentration is 140 mg / L, C / N is 10, at 30 ℃, 120rpm, cultured for 53 hours, OD 600 rose to 1.6, TN removal rate re...
Embodiment 3
[0049] Embodiment 3: the removal ability of Acinetobacter baumannii AL-6 to nitrate nitrogen in wastewater
[0050] Acinetobacter baumannii AL-6 used nitrate as nitrogen source, and the aerobic denitrification ability of the strain was investigated by detecting the degradation of nitrogen source in wastewater. The initial TN concentration of nitrate wastewater was 80.8 mg / L, and the initial NO 3 - The -N concentration was 79.2 mg / L, the initial C / N ratio was 10, the pH was controlled at 7-8, and the cultivation was carried out at 30 °C and 120 rpm. After 48 h, TN removed 48.2%, NO 3 - -N removed 50.2%. The experimental results indicated that the strain AL-6 could carry out aerobic denitrification with nitrate nitrogen as the substrate under aerobic conditions. see attached Figure 4 .
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