| Front page | | Contents | | Previous | | Next |
Model assessment of reductive dechlorination as a remediation technology for contaminant sources in fractured clay: Modeling tool
Appendix F Model verification – analytical solution
The numerical model is verified by comparing results to an analytical solution for a system of parallel fractures [Sudicky and Frind, 1982]. This analytical solution is also used in SprækkeJAGG [SprakkeJAGG, 2008] and gives the exact solution for concentration in the fracture and matrix at steady-state with a constant concentration at the fracture inlet. In this model, the transport in the matrix is assumed to be one-dimensional in the direction perpendicular to the matrix. Furthermore the degradation rate is assumed to be a 1st order. The parameters used in this verification are listed in Table F.1.
Table F.1 - Parameters used for the model verification
Parameters |
Symbol |
Value |
Unit |
Net recharge |
I |
0.1 |
m/year |
Fracture spacing |
2B |
0.2 |
m |
Fracture aperture |
2b |
0.001 |
m |
Water velocity in fracture |
vf |
20 |
m/year |
Matrix porosity |
φ |
0.33 |
- |
Longitudinal dispersivity in fracture |
αL |
0.1 |
m |
Fracture dispersion coefficient |
Df |
2 |
m²/year |
Matrix diffusion coefficient |
Dm |
0.0066 |
m²/year |
Degradation rate |
λ |
0.5 |
year-1 |
Start concentration |
C0 |
1400 |
mg/L |

Figure F.1 – Contaminant concentration at different distances from the fracture for the numerical model (line) and analytical solution (symbol) for the parameters given in Table F.1
| Front page | | Contents | | Previous | | Next | | Top |
Version 1.0 July 2009, © Danish Environmental Protection Agency
|