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Waste Water Treatment Plant Case Study
Aartselaar
Aquafin
MAIS AL JUBORI
HANNES DECADT
MOHAMMED HERZALLAH
1
April 2015
Outline
 Introduction
 General Scheme of the WWTP
 Description of the WWTP
 Calculations
 Problems and Possible Solutions
 Conclusion
2
Introduction
 Aquafin is a regional wastewater treatment company in
Flanders.
 Mission: expanding, operating and financing the sewage
treatment infrastructure in Flanders.
 responsible for the operation of 287 sewage treatment
plants distributed over the 5 provinces of Flanders.
 Each plant recives household wastewater collected
from the municipal sewers and treats it according to the
European and Flemish standards.
 Aquafin Aartselaar is one of these plants, located in
province of Antwerp and serves the population of the
zone Aartselaar and part of Wilrijk using the biological
treatment.
3
GENERAL
SCHEME
OF THE
WWTP
Aartselaar
4
Description of the WWTP
A. Collectors and screw system
B. Sand traps
C. Selector, anaerobic and anoxic tank
D. Aeration tanks
E. Sedimentation tanks
F. Sludge handling
5
screw system
Sand traps
Selector tank
Anaerobic tank
Aeration tank with surface aerator
Sedimentation tank
F
A B C
D E
Calculations
Nitrification-denitrification
6
Nitrification:
NH4
+ O2  NO3
-
Denitrification:
NO3
- N2
Unaerated tanks Aeration tanks
Recycling
Selector
Anaerobic
Anoxic
Facultative aerated
Aerobic
Calculations
Phosphate removal
7
Growth
P-uptake
Selector
Anaerobic
Anoxic
Facultative aerated
Aerobic
PHB forming
P-release
Unaerated tanks Aeration tanks
Recycling
Calculations
Removal efficiencies
8
Qinf = 28875 m³/d
= 5962 m³/d
G
= 444 m³/d
TT
= 28818 m³/d=51788 m³/d
Xt = 70 kg/m³
= 28488 m³/d
= 22526 m³/d
= 22970 m³/d
Qtot = 57750 m³/d
Unaerated tanks
2500 m³
Aeration tanks
5600 m³
Settle tanks
4242 m³
Xeff = 14.6 g/m³X = 4 kg/m³
= 387 m³/d
= 57 m³/d
Xw = 9 kg/m³
Qsi
Qr’
Qr
Qr+Qr’
Qreflow G+TT
Qt
Qso
Qw
Qeff
ΔX=4000 kg sludge/d
Calculations
Flow scheme
Calculations
Sludge-related parameters
10
Calculations
Oxygen demand & aeration costs
11
30%
€0.15/kWh
Problems and Possible Solutions
 The high concentration of the suspended solids in the effluent
 Poor nitrogen removal
12
- Improving NH4
+-removal: longer sludge residence time
- Improving NO3
--removal: recycling more or making the anoxic zone larger
- Turn-off the paddlers of the aeration tanks to let the sludge settle down
calmly
- Use of membranes
Conclusion
 Typical conventional activated sludge system with recycling
for biological treatment of COD, nitrogen and phosphate
 Removal efficiencies reach the actual quota, but can be
bettered:
 The COD is removed properly
 Concentration of suspended solids has to be carefully followed
up
 Removal of nitrogen could be improved by more recycling
 Biological phosphate removal works satisfied
13

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Aartselaar Aquafin water , Environmental water plant .

  • 1. Waste Water Treatment Plant Case Study Aartselaar Aquafin MAIS AL JUBORI HANNES DECADT MOHAMMED HERZALLAH 1 April 2015
  • 2. Outline  Introduction  General Scheme of the WWTP  Description of the WWTP  Calculations  Problems and Possible Solutions  Conclusion 2
  • 3. Introduction  Aquafin is a regional wastewater treatment company in Flanders.  Mission: expanding, operating and financing the sewage treatment infrastructure in Flanders.  responsible for the operation of 287 sewage treatment plants distributed over the 5 provinces of Flanders.  Each plant recives household wastewater collected from the municipal sewers and treats it according to the European and Flemish standards.  Aquafin Aartselaar is one of these plants, located in province of Antwerp and serves the population of the zone Aartselaar and part of Wilrijk using the biological treatment. 3
  • 5. Description of the WWTP A. Collectors and screw system B. Sand traps C. Selector, anaerobic and anoxic tank D. Aeration tanks E. Sedimentation tanks F. Sludge handling 5 screw system Sand traps Selector tank Anaerobic tank Aeration tank with surface aerator Sedimentation tank F A B C D E
  • 6. Calculations Nitrification-denitrification 6 Nitrification: NH4 + O2  NO3 - Denitrification: NO3 - N2 Unaerated tanks Aeration tanks Recycling Selector Anaerobic Anoxic Facultative aerated Aerobic
  • 9. Qinf = 28875 m³/d = 5962 m³/d G = 444 m³/d TT = 28818 m³/d=51788 m³/d Xt = 70 kg/m³ = 28488 m³/d = 22526 m³/d = 22970 m³/d Qtot = 57750 m³/d Unaerated tanks 2500 m³ Aeration tanks 5600 m³ Settle tanks 4242 m³ Xeff = 14.6 g/m³X = 4 kg/m³ = 387 m³/d = 57 m³/d Xw = 9 kg/m³ Qsi Qr’ Qr Qr+Qr’ Qreflow G+TT Qt Qso Qw Qeff ΔX=4000 kg sludge/d Calculations Flow scheme
  • 11. Calculations Oxygen demand & aeration costs 11 30% €0.15/kWh
  • 12. Problems and Possible Solutions  The high concentration of the suspended solids in the effluent  Poor nitrogen removal 12 - Improving NH4 +-removal: longer sludge residence time - Improving NO3 --removal: recycling more or making the anoxic zone larger - Turn-off the paddlers of the aeration tanks to let the sludge settle down calmly - Use of membranes
  • 13. Conclusion  Typical conventional activated sludge system with recycling for biological treatment of COD, nitrogen and phosphate  Removal efficiencies reach the actual quota, but can be bettered:  The COD is removed properly  Concentration of suspended solids has to be carefully followed up  Removal of nitrogen could be improved by more recycling  Biological phosphate removal works satisfied 13

Notas del editor

  1. Explanation by improving NH4-removal: Now the sludge residence time is 7.3 days, which is rather short if good nitrification is desired, because nitrifying bacteria are slow growers. The sludge residence time can be made longer by diminishing the Qwaste (Especially the NO3-removal should be bettered, but the NH4 effluent is not zero so can also be bettered)