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3.2 Materials and methods


               and used cultivar values recommended for STICS    46  while the agricultural practises
               were prescribed according to the experimental data available. Pesticide properties
               were set according to measured data when possible (Table 3.3).



                  Pesticide    Solubility   Koc           Kne ads     Kne des           DT50
                                               3
                                      -3
                                                  -1
                                                                       -1
                                                           -1
                                                                                     -1
                               mg/dm        dm kg         d           d        KJmol   d
                  Atrazine     35           70              0.9       0.6      45.4     26
                  references   42           57              20        20       60       57
                  Isoproturon   70.2        40              0.85      0.085    46.8     25
                  references   42           42              59        59       60       56
                  bentazone    570          5.5             0.0       0.0      73.8     62
                  references   42           55              -         -        60       62

               Table 3.3 – Pesticide characteristics used : Koc soil organic carbon sorption co-
                             efficient, non-equilibrium sorption (Kneads) and disorption (knedes)
                             coeefficient, the molar enthalpy for transformation, DT50 degrada-
                             tion time for 50% opf compound


                  The Koc value for Bentazone was graphically determined from the laboratory
               measurements provided by Boesten and Van der Pas.      55  The non-equilibrium sorp-
               tion was not taken into account for bentazon because of the weak sorption of the
               bentazon onto the soil particles. Non–equilibrium sorption rate are difficult to mea-
               sure and data available in the literature are very scarces. The values selected for
               atrazine were provided by Rat.    20  For isoproturon, as suggested by Guimont,   56
               we used a ratio of 10 between desorption and sorption at non-equilibium, and the
               sorption rate was set to 0.85 according to the adsorption rate recommended for
               chlortoluron by Altfelder.  59  The DT50 for the three pesticides selected were esta-
               blished from batch experiments in the laboratory. The molar enthalpy values were
               taken from EFSA.    60  A 3-year spin-up was used to reach realistic initial values for
               soil moisture.


               3.2.5 Model evaluation methodology

                  The methodology for evaluatingthe model is divided into two approaches, the
               firstbeing a graphical display comparison and the second is a statistical analysis
               with the criteria detailed in this subsection. The statistical indicators selected for
               the model assessment are the Root Mean Square Error (RMSE), The Modelling
               Efficiency (EF), the Bias (ERR) and the Pearson Correlation Coefficient (CR).


                                                     100     s  P (P i − O i )
                                        RMSE =        ¯   ×                                (3.2.10)
                                                     O              n




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