Analysis of the crystallization kinetics with Ziabicki model reveals maximum of the steady-state crystallization rate of β phase as 2200 s−1 at 22 °C, and the highest crystallization rate of α phase as 200 s−1 at 70 °C.
Numerical optimization of the model revealed a maximum reduction of 71, 93, 86 and 99.6 % COD, phosphate, color and sulfate at optimal FeCl3 dosage = 3 g/l, pH 8, and reaction time = 95 min.
The data -expressed relative to the first stage- revealed maximum change during stage III (ripe).
Numerical optimization of the model revealed that the maximum reduction of 71, 93, 86 and 99.6 % COD, phosphate, color and sulfate could be achieved respectively at optimal FeCl3 dosage = 3 g/l, pH 8, and reaction time = 95 min; whereas the average EC (mS/cm), TDS (ppt) and salt (ppt) concentration in the effluent were 8.29, 6.35 and 4.35.
The HRF+TD model revealed a global maximum in the left-temporal lobe with a positive response and additional, mostly remote, clusters with negative responses.
Surface and contour plots of the regression models revealed a maximum hydrogen production rate of 0.566 mmol H2/L/h at 27.5 °C and 287 W/m2 and a maximum hydrogen yield of 0.326 mol H2/mol substrate at 26.8 °C and 285 W/m285
Fitting the model revealed that the profile of estimated population asbestos exposure over time had several local maxima, whereas in previous analyses the profile increased monotonically before the peak year and decreased monotonically thereafter.
What this model revealed was remarkable.
The model revealed three distinct growth phases.
Comparison of the results from the physical and ANN models revealed that the maximum average and average relative errors computed for the validation data set were 19.8% and 15.9%, respectively.
