Low-temperature aerobic denitrifying strain Pseudomonas psychrophila Den-03 and screening method and application thereof
A technology of aerobic denitrification bacteria and aerobic denitrification, applied in the direction of chemical instruments and methods, biochemical equipment and methods, methods based on microorganisms, etc., to achieve the effects of reducing production energy consumption, simple activation, and improving nitrogen conversion rate
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specific Embodiment approach 1
[0025] Specific implementation mode 1: This implementation mode provides screening steps for aerobic denitrifying bacteria
[0026] 1. In winter, take 10mL of fresh activated sludge from the Harbin Municipal Sewage Plant and add it to a 100mL aerobic denitrification medium in a triangular flask, and place it at a temperature of 10 oC. Cultivate for 48 hours in a shaker with a rotating speed of 150r / min to obtain the enriched bacterial solution; 2. Take 10mL of the enriched bacterial solution and add it to a 100mL aerobic denitrification medium conical flask, repeat the culture conditions of step 1 to obtain the domesticated bacteria 3. Take 100 μL of domesticated bacteria solution and add it to the solid aerobic denitrification medium plate, spread it evenly by coating method, and place it at a temperature of 10 o In the incubator of C, cultivate for 48-72 hours to obtain a single colony; 4. Repeat the operation step 3 3-4 times to complete the acquisition of low-temperature a...
specific Embodiment approach 2
[0030] Specific embodiment two: take the single colony of low-temperature aerobic denitrifying bacteria obtained in specific embodiment one and culture it in low-temperature aerobic denitrification medium equipped with sterilized aerobic denitrification medium for 96 hours, and the rotating speed is 150r / min, which is low-temperature aerobic Growth and degradation curves of denitrifying bacteria. The result is as figure 1 Shown, 96h aerobic denitrifier OD 600 tends to be stable at around 1. The pollutant degradation rate reached 70%, indicating that the aerobic denitrifying bacteria obtained in this embodiment have good degradation ability.
specific Embodiment approach 3
[0031] Embodiment 3: The difference from Embodiment 2 is that the aerobic denitrifying bacteria liquid after 96 hours of cultivation is placed in the SBR reactor. According to four different nitrate nitrogen concentration 100mg / L, 80mg / L, 60mg / L, 40mg / L respectively pack in four conical flask SBR reactors, add 10% activated sludge in each 500mL conical flask, 10 o C culture, 150 r / min, aerobic culture for 10 days. Reaction cycle: a cycle of 12 hours, water intake 0.5 hours, aeration 8 hours, sedimentation 2 hours, drainage and idle time 1.5 hours. The result is as figure 2 As shown, with the prolongation of the culture time, the degradation effect of different concentrations of nitrate nitrogen was obvious in 8 days, and the concentration of nitrate nitrogen all reached below 20mg / L, indicating that the low-temperature aerobic denitrification bacteria used in this implementation have good denitrification ability.
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