Figures & data
Fig. 1 The model-independent model application and evaluation framework that can be used in southern Africa.
![Fig. 1 The model-independent model application and evaluation framework that can be used in southern Africa.](/cms/asset/829c03fb-0d40-4037-a965-383188b86d77/thsj_a_690881_o_f0001g.gif)
Table 1 List of the parameters of the Pitman model including those of the reservoir water balance model (Hughes et al. 2006)
Fig. 2 A flow diagram of the Pitman model, indicating the main components of the model including the parameters (given in brackets).
![Fig. 2 A flow diagram of the Pitman model, indicating the main components of the model including the parameters (given in brackets).](/cms/asset/9a8b6746-373f-4ed6-818d-2db5d997d8d6/thsj_a_690881_o_f0002g.jpg)
Table 2 The information typically included in the South Africa AGIS land type database (AGIS Citation2007)
Fig. 3 The incorporation of uncertainty in the a priori parameter estimation procedure of the Pitman model. A secondary variable is a basin-scale equivalent of a variable that is measured at point scale.
![Fig. 3 The incorporation of uncertainty in the a priori parameter estimation procedure of the Pitman model. A secondary variable is a basin-scale equivalent of a variable that is measured at point scale.](/cms/asset/692a6a5d-b55d-4363-b873-64975be8483a/thsj_a_690881_o_f0003g.jpg)
Table 3 Details of the regional Budyko type relationships based on simulated and naturalized observed data. Equations are of the form ln(Q/P) = a × ln(P/PE) + b
Fig. 4 Hydrological metrics used to constrain model output ensembles. The regional relationships between (a) Q/P and P/PE based on observed flows, and (b) the resultant regions. (c) Slope of FDC relationship with aridity and relief, including the 90% prediction limits. (d) Range of groundwater recharge estimates between the lowest and the middle values (grey) and between the middle and the highest values (black).
![Fig. 4 Hydrological metrics used to constrain model output ensembles. The regional relationships between (a) Q/P and P/PE based on observed flows, and (b) the resultant regions. (c) Slope of FDC relationship with aridity and relief, including the 90% prediction limits. (d) Range of groundwater recharge estimates between the lowest and the middle values (grey) and between the middle and the highest values (black).](/cms/asset/0e65ce84-3206-40ee-ae58-f2d9b8487e67/thsj_a_690881_o_f0004g.gif)
Table 4 Percentage frequency of occurrence of possible outcome types A to E in the comparison of the model output ensembles with the constraints
Fig. 5 Possible outcome types (A to E) from an analysis of uncertainty in the parameter estimation process against the uncertainty related to the constraints (* is the intersection between the parameter priors and the regional constraints).
![Fig. 5 Possible outcome types (A to E) from an analysis of uncertainty in the parameter estimation process against the uncertainty related to the constraints (* is the intersection between the parameter priors and the regional constraints).](/cms/asset/ae0e0b6a-a389-48bb-a245-94d4a82368e5/thsj_a_690881_o_f0005g.gif)
Fig. 6 Results of the comparison of the uncertainty between the runoff ratio constraint and the parameter estimation for the basins in regions 1–5. The observed data points are plotted for comparison with range of simulations, while the upper and lower 90% bounds are 95th and 5th prediction limits of the regression equations of the constraints.
![Fig. 6 Results of the comparison of the uncertainty between the runoff ratio constraint and the parameter estimation for the basins in regions 1–5. The observed data points are plotted for comparison with range of simulations, while the upper and lower 90% bounds are 95th and 5th prediction limits of the regression equations of the constraints.](/cms/asset/501c3897-2c6b-4b01-befe-23b38839401c/thsj_a_690881_o_f0006g.gif)
Fig. 7 Results of the comparison of the uncertainty between the FDC constraint and the parameter estimation for the test basins.
![Fig. 7 Results of the comparison of the uncertainty between the FDC constraint and the parameter estimation for the test basins.](/cms/asset/8ebceb37-83c9-4125-88e5-444bbc0d992b/thsj_a_690881_o_f0007g.gif)
Fig. 9 Illustration of the sensitivity analysis of the ensembles using a priori parameter estimates for parameter ZMIN for sub-basin R20C, showing the calculation of the sensitivity class of the parameters based on either traditional objective functions or constraint metrics.
![Fig. 9 Illustration of the sensitivity analysis of the ensembles using a priori parameter estimates for parameter ZMIN for sub-basin R20C, showing the calculation of the sensitivity class of the parameters based on either traditional objective functions or constraint metrics.](/cms/asset/438066a0-1e8c-4ff4-9de5-0ce165b77696/thsj_a_690881_o_f0009g.gif)
Fig. 10 Results of the sensitivity analysis for some of the selected sub-basins used in the study. Black indicates a critical (highly sensitive) parameter, grey is important (sensitive) and white is negligible (insensitive).
![Fig. 10 Results of the sensitivity analysis for some of the selected sub-basins used in the study. Black indicates a critical (highly sensitive) parameter, grey is important (sensitive) and white is negligible (insensitive).](/cms/asset/0ef67950-ed63-4334-ba6a-d40174e9cd39/thsj_a_690881_o_f0010g.gif)
Fig. 11 The variation in the range of: (a) mean monthly runoff and (b) FDC slope, before and after the calibration of the GW parameter. Uncertainty range refers to the difference between the maximum and minimum mean monthly runoff and FDC slope values related to simulation ensembles.
![Fig. 11 The variation in the range of: (a) mean monthly runoff and (b) FDC slope, before and after the calibration of the GW parameter. Uncertainty range refers to the difference between the maximum and minimum mean monthly runoff and FDC slope values related to simulation ensembles.](/cms/asset/de48ba08-2c30-45f4-bc01-5ad8fa5e3baf/thsj_a_690881_o_f0011g.gif)