Paracoccus denitrifican with denitrification and iron reduction functions and culturing method and application thereof
A technology for denitrifying paracoccus and its cultivation method, which is applied in the field of denitrifying paracoccus ZGL1 and its cultivation, which can solve the problems of increased operating costs and achieve the effects of less investment and operating costs, strong practical value, and simple processes
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Embodiment 1
[0021] Embodiment 1: Denitrification of heterotrophic denitrification wastewater by strains of the present invention under organic carbon source conditions
[0022] Organic carbon source denitrification medium: MgSO 4 ·7H 2 O 5 mM, CaCl 2 2H 2 O 5 mM, NH 4 Cl 0.28 g / L, KH 2 PO 4 0.25 g / L, NaHCO 3 5.4 g / L, KNO 3 10 mM, glucose 5 mM, adjust the pH to 7.2~7.4, and the culture medium is sterilized.
[0023] Using an organic carbon source denitrification medium, inoculate the strain ZGL1 with a dry weight of 0.6 g / L under anaerobic conditions and cultivate it at 30°C. Samples were taken at regular intervals to determine the change of nitrate concentration. The results are shown in Table 1. It can be seen from Table 1 that in the presence of organic carbon sources, the denitrification speed is fast and the efficiency is high. After 24 hours of cultivation, 94.9% of the nitrate in the system was removed.
[0024] Table 1 Effect of strain ZGL1 on heterotrophic denitrificat...
Embodiment 2
[0026] Example 2: Simultaneous heterotrophic denitrification waste gas denitrification and iron reduction by the strain of the present invention under the condition of organic carbon source
[0027] Organic carbon source denitrification iron reduction medium: MgSO 4 ·7H 2 O 5 mM, CaCl 2 2H 2 O 5 mM, NH 4 Cl 0.28 g / L, KH 2 PO 4 0.25 g / L, NaHCO 3 5.4 g / L, glucose 5 mM, Fe II EDTA-NO 4 mM, Fe III EDTA 10mM, adjust the pH to 7.2~7.4, and the culture medium is sterilized.
[0028] Use the organic carbon source denitrification iron reduction medium, inoculate the strain ZGL1 with a dry weight of 0.6g / L under anaerobic conditions, cultivate it at 30°C, and take samples at regular intervals to measure Fe II EDTA-NO and Fe III The changes of EDTA concentration, the results are shown in Table 2. It can be seen from Table 2 that after 12 h of cultivation, Fe II EDTA-NO and Fe III EDTA was well reduced, Fe II EDTA-NO reduction rate is 80.3%, Fe III EDTA is 55.8%. Strain ...
Embodiment 3
[0031] Embodiment 3: Denitrification of sulfur autotrophic denitrification wastewater by bacterial strains of the present invention
[0032] Sulfur autotrophic denitrification medium: MgSO 4 ·7H 2 O 5 mM, CaCl 2 2H 2 O 5 mM, NH 4 Cl 0.28 g / L, KH 2 PO 4 0.25 g / L, NaHCO 3 5.4 g / L, KNO 3 10 mM, Na 2 S 2 o 3 ·5H 2 O 5 mM, adjust the pH to 7.2~7.4, and the culture medium is sterilized.
[0033] Use the organic carbon source denitrification iron reduction medium, inoculate the strain ZGL1 with a dry weight of 0.6g / L under anaerobic conditions, cultivate it at 30°C, and take samples at regular intervals to measure NO 3 - and S 2 o 3 2- The changes in concentration are shown in Table 3. It can be seen from Table 3 that strain ZGL1 can not only grow under heterotrophic conditions, but also grow under autotrophic conditions. The initial concentration was 10 mM NO 3 - and 5 mM S 2 o 3 2- , strain ZGL1 can carry out sulfur autotrophic denitrification process, aft...
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