Citation: | Nguyen Van Hoang. 2021. Determination of groundwater solute transport parameters in finite element modelling using tracer injection and withdrawal testing data. Journal of Groundwater Science and Engineering, 9(4): 292-303. doi: 10.19637/j.cnki.2305-7068.2021.04.003 |
The groundwater tracer injection and withdrawal tests are often carried out for the determination of aquifer solute transport parameters. However, the parameter analyses encounter a great difficulty due to the radial flow nature and the variability of the temporal boundary conditions. An adaptive methodology for the determination of groundwater solute transport parameters using tracer injection and withdrawal test data had been developed and illustrated through an actual case. The methodology includes the treatment of the tracer boundary condition at the tracer injection well, the normalization of tracer concentration, the groundwater solute transport finite element modelling and the method of least squares to optimize the parameters. An application of this methodology was carried out in a field test in the South of Hanoi city. The tested aquifer is Pleistocene aquifer, which is a main aquifer and has been providing domestic water supply to the city since the French time. Effective porosity of 0.31, longitudinal dispersivity of 2.2 m, and hydrodynamic dispersion coefficients from D = 220 m2/d right outside the pumping well screen to D =15.8 m2/d right outside the tracer injection well screen have been obtained for the aquifer at the test site. The minimal sum of squares of the differences between the observed and model normalized tracer concentration is 0.00119, which is corresponding to the average absolute difference between observed and model normalized concentrations of 0.035 5 (while 1 is the worst and 0 is the best fit).
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Location map of the study area
Testing wells' scheme, location and Pleistocene aquifer on fresh-brackish boundary
Hydrogeological section through the testing wells
Well log of central well CHN5
GW TDS in the injection well
TDS of the pumped out GW
GW flow through the injection well section
Breakthrough curves of TDS in injection and pumping wells
The transformation of absolute solute concentration into normalized solute concentration
Drawdown curve of the pumping well QS-5A 13 (Tong Thanh Tung, 2015)
The average least squares and corresponding effective porosity and longitudinal dispersivity
Absolute solute concentration in the pumped GW and outside the pumping well screen corresponding to the minimal least squares
Normalized solute concentration in the pumped GW and outside the pumping well screen corresponding to the minimal least squares