Razi Epsztein
- R. Epsztein, M. Beliavski, S. Tarre, M. Green
September 2016 Technion – Israel Institute of Technology
Razi Epsztein R. Epsztein, M. Beliavski, S. Tarre, M. Green Technion - - PowerPoint PPT Presentation
Razi Epsztein R. Epsztein, M. Beliavski, S. Tarre, M. Green Technion Israel September 2016 Institute of Technology Short background Nitrate pollution (>10 mg NO3 N/L according to EPA) Physicochemical methods (RO, IEX,
September 2016 Technion – Israel Institute of Technology
Nitrate reduction to N2 gas by denitrifying bacteria under
Electron donor can be organic or inorganic and must be
Cell Yields are lower for autotrophic bacteria using inorganic
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Lee & Rittman, 2002
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Denitrification rates < 1 g N /(Lreactorx day)
Influent Effluent
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N2 pressure increases H2 pressure decreases Denitrfication rate decreases Purging with H2 is required Safety problem Financial problem
0,5 1 1,5 2 2,5 5 10 15 20 25 Developed N2 pressure [bars] Removed NO3
Henry’s law: P = H x C H [bar * L / mg]
At 20˚C
15 20 25 30 35 40 N2 [mg/L] NO3‐N: 25 mg/L NO3‐N: 25 mg/L N2: 15 mg/L N2: 15 mg/L NO3‐N: 25 mg/L NO3‐N: 10 mg/L N2: 15 mg/L N2: 30 mg/L
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Main Characteristics:
(economic and safe)
bacterial growth
continuous operation
0,5 1 1,5 2 2,5 20 40 60 80 100 120 Partial pressure [bars] Time [hours] H2 N2
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Steady state
Influent: 25 mg N/L Effluent: 10 mg N/L Total pressure: 3 bars
H2 utilization > 90%
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