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PARAMETER ESTIMATION OF THE POLLUTANT REMOVAL MECHANISMS OF SUBSURFACE HORIZONTAL FLOW CONSTRUCTED WETLANDS TREATING GREYWATER  Dr. Shiromi Karunarathne MKBS Wijesiri  VM Jayasooriya
Think Ecologically……. Reduce  Reuse  Recycle
CONTENTS ,[object Object],[object Object],[object Object],[object Object],[object Object]
INTRODUCTION ,[object Object],[object Object],[object Object],[object Object]
INTRODUCTION cont. ,[object Object],[object Object],[object Object]
OBJECTIVES ,[object Object],[object Object],[object Object]
OBJECTIVES cont. ,[object Object],[object Object]
MATERIALS AND METHODS ,[object Object],[object Object],[object Object],[object Object],[object Object]
DESIGN OF SHF CW SAMPLING POINT 01 SAMPLING POINT 04 SAMPLING POINT 03 SAMPLING POINT 02
MATERIALS AND METHODS cont. ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],MATERIALS AND METHODS cont.
Assuming  first order kinetics  prevail, ( C e  / C i ) = e -K T t   C a  = C e  {(1- e -K T t ) / e -K T t } .………....….. (2) Where; K T  –  temperature dependent reaction rate  constant t  –  retention time Then differentiate the equation (2) w.r.t. K T  and simplify the equation; d(C e )/ d(K T ) = - tC e  …...………...….... (3)
Effective sizing of the constructed wetland Then differentiate the equation (2) w.r.t. t and simplify the equation; d(C e )/d(t) = -K T C e  ………………….... (4) Maximum retention time is taken that would yield satisfactory levels of treatment, Q = V/t max  …………….......................... (5) A = Q.t max  /d …………......................... (6) Then, resized surface area can be calculated using above equations.
RESULTS Variation of weekly COD  Variation of weekly BOD
Variation of weekly  nitrate nitrogen  Variation of weekly  nitrite nitrogen
Variation of weekly  total kjeldhal nitrogen Variation of weekly  total phosphorous
Variation of weekly  total coliforms  Variation of weekly  total suspended solids
Estimation of reaction rate constants (K T ) using  dessolver 1.7 Graphical representation of the variation of effluent BOD 5  against K T (BOD )
Estimated reaction rate constants     Parameter Temperature dependant reaction rate constant – K T  (day -1 )±SD BOD 5 0.80799 ± 0.070 COD 0.61166 ± 0.062 Nitrate Nitrogen 0.80131 ± 0.024 Nitrite Nitrogen 0.85634 ± 0.010 Total Kjeldhal Nitrogen 0.28327 ± 0.050 Total Phosphorous 0.34343 ± 0.078 Total Suspended Solids 0.38157 ± 0.095
Estimation of optimum retention time (t opt ) Estimation of optimum retention time (t) for BOD
Estimated retention time for each parameter   Parameter (Reference)   Retention time – t (day)   BOD 5  (50 mg/l) 3.150 COD (250 mg/l) 2.100 Nitrate Nitrogen (1 mg/l) 3.125 Nitrite Nitrogen (0.005 mg/l) 3.375 Total Kjeldhal Nitrogen (1.2 mg/l) 2.850 Total Phosphorous (3.5 mg/l) 2.525 Total Suspended Solids (30 mg/l) 3.067
RESULTS cont. ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
EFFECT OF LOADING RATE ,[object Object],[object Object],[object Object],[object Object]
Conclusion ,[object Object],[object Object],[object Object]
L E T’S  G O G R E EN for a better world Thank You

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Parameter Estimation of Pollutant Removal for Subsurface Horizontal Flow Constructed Wetlands Treating Greywater

  • 1. PARAMETER ESTIMATION OF THE POLLUTANT REMOVAL MECHANISMS OF SUBSURFACE HORIZONTAL FLOW CONSTRUCTED WETLANDS TREATING GREYWATER Dr. Shiromi Karunarathne MKBS Wijesiri VM Jayasooriya
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  • 11. DESIGN OF SHF CW SAMPLING POINT 01 SAMPLING POINT 04 SAMPLING POINT 03 SAMPLING POINT 02
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  • 14. Assuming first order kinetics prevail, ( C e / C i ) = e -K T t C a = C e {(1- e -K T t ) / e -K T t } .………....….. (2) Where; K T – temperature dependent reaction rate constant t – retention time Then differentiate the equation (2) w.r.t. K T and simplify the equation; d(C e )/ d(K T ) = - tC e …...………...….... (3)
  • 15. Effective sizing of the constructed wetland Then differentiate the equation (2) w.r.t. t and simplify the equation; d(C e )/d(t) = -K T C e ………………….... (4) Maximum retention time is taken that would yield satisfactory levels of treatment, Q = V/t max …………….......................... (5) A = Q.t max /d …………......................... (6) Then, resized surface area can be calculated using above equations.
  • 16. RESULTS Variation of weekly COD Variation of weekly BOD
  • 17. Variation of weekly nitrate nitrogen Variation of weekly nitrite nitrogen
  • 18. Variation of weekly total kjeldhal nitrogen Variation of weekly total phosphorous
  • 19. Variation of weekly total coliforms Variation of weekly total suspended solids
  • 20. Estimation of reaction rate constants (K T ) using dessolver 1.7 Graphical representation of the variation of effluent BOD 5 against K T (BOD )
  • 21. Estimated reaction rate constants     Parameter Temperature dependant reaction rate constant – K T (day -1 )±SD BOD 5 0.80799 ± 0.070 COD 0.61166 ± 0.062 Nitrate Nitrogen 0.80131 ± 0.024 Nitrite Nitrogen 0.85634 ± 0.010 Total Kjeldhal Nitrogen 0.28327 ± 0.050 Total Phosphorous 0.34343 ± 0.078 Total Suspended Solids 0.38157 ± 0.095
  • 22. Estimation of optimum retention time (t opt ) Estimation of optimum retention time (t) for BOD
  • 23. Estimated retention time for each parameter   Parameter (Reference)   Retention time – t (day)   BOD 5 (50 mg/l) 3.150 COD (250 mg/l) 2.100 Nitrate Nitrogen (1 mg/l) 3.125 Nitrite Nitrogen (0.005 mg/l) 3.375 Total Kjeldhal Nitrogen (1.2 mg/l) 2.850 Total Phosphorous (3.5 mg/l) 2.525 Total Suspended Solids (30 mg/l) 3.067
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  • 27. L E T’S G O G R E EN for a better world Thank You