3.3.3.1. Goodness of Fit Statistical Analysis
Evaluating statistics is essential for assessing model performance, as they quantify how effective the model explains variability in recovery rates and grades. The fit statistics for nickel, copper, zinc, and lead recoveries, presented in
Table 5, provide a rigorous assessment of the RSM model’s effectiveness in flotation analysis.
The R² values indicate that the model explains 61.44%, 56.05%, 53.54%, and 31.25% of variability in recoveries for Ni, Cu, Zn, and Pb, respectively. While moderate fits are noted for nickel, copper, and zinc, the low R² for lead signifies unexplained variability, indicating a need for additional factors or interactions not captured by the current model. Adjusted R² values are also low (0.2546 for nickel, 0.1503 for copper, 0.1019 for zinc, and 0.2025 for lead), pointing to possible overfitting and the necessity for model simplification. Negative predicted R² values for nickel, copper, and zinc further raise concerns regarding predictive reliability, whereas the positive predicted R² for lead reflects only marginal predictive capacity. Adequate precision values ranging from 4.88 to 5.65 suggest that the model provides reasonable indication of response. Refinement through the inclusion of the additional relevant variables or reassessment of experimental conditions is essential to enhance predictive accuracy and optimize flotation performance.
The analysis of fit statistics for nickel, copper, zinc, and lead grades, presented in
Table 6, offers further insights into the RSM model’s performance. These results highlight the model’s capacity to explain variability in grade outcomes and complement the recovery analysis, there by offering a more comprehensive evaluation of flotation efficiency.
The R² values of 0.5390 (Ni) , 0.7006 (Cu), 0.5371 (Zn) , and 0.5626 Pb indicated varied explanatory power, with copper showing the strongest fit and lead requiring refinement. Adjusted R² values are notably low for nickel (0.1087) and zinc (0.1050), suggesting overfitting and limited reliability. Negative predicted R² values for nickel, copper, zinc, and lead further question the model’s robustness, while adequate precision values (4.50 to 7.05) provide only moderate confidence. Overall, these results underscore the need for model refinement through inclusion of additional variables and improved experimental design.
3.3.3.2. Analysis of Variance (ANOVA) of the Overall Model
Table 7 and
Table 8 presents the analysis of variance (ANOVA) for the recovery and grades of nickel, copper, zinc, and lead from UG2 ore flotation. ANOVA was employed to identify significant differences among group means and to evaluate the impact of key factors - collector dosage (A), depressant dosage (B), pulp pH (C), and flotation time (D) - on recovery rates and metal grades.
For nickel recovery, the overall model was not significant, though flotation time was influential (F-value = 7.26, p-value = 0.0167), with a favourable lack of fit indicating good data alignment. Copper recovery also lacked overall significance, but the interaction between depressant dosage and flotation time (BD, F-value = 4.76, p-value = 0.0455), and the quadratic term for depressant dosage (B², F-value = 4.96, p-value = 0.0417), were significant, with an adequate lack of fit. Zinc recovery was non-significant overall, yet depressant dosage and its quadratic term were significant (F-value = 5.36, p-value = 0.0351; F-value = 9.36, p-value = 0.0079), though the significant lack of fit indicated the need for additional factors. Lead recovery showed a significant model (F-value = 2.84, p-value = 0.0454), driven largely by flotation time (F-value = 7.87, p-value = 0.0096), with a non-significant lack of fit supporting model adequacy.
The nickel grade model was non-significant, with a significant lack of fit (F-value = 8.26, p-value = 0.0155) indicating poor representation of factors affecting Ni grade. In contrast, the copper grade model was significant (F-value = 2.51, p-value = 0.0441), driven by pulp pH (C) and flotation time (D) and the interaction between collector dosage and flotation time (AB) (F-value = 5.98, p-value = 0.0273), though its lack of fit suggests missing factors. The zinc grade model was again non-significant overall, with all individual factors yielding non-significant results, and its lack of fit not significant (F-value = 0.4133, p-value = 0.8902), indicating adequate alignment but limited predictive capacity. The lead grade model also lacked overall significance, though flotation time (D) was significant (F-value = 4.81, p-value = 0.0445), with a non- significant lack of fit supporting model accuracy. Overall, copper and lead grades show meaningful factor effects, while nickel and zinc grade models fail to capture variability, highlighting the need for refinement.
3.3.3.3. Empirical Model Equations
The empirical model equations (1 – 8) were developed using CCD to predict the recovery and grade of Ni, Cu, Zn and Pb as functions of collector dosage (A), depressant dosage (B), pulp pH (C), and flotation time (D). These equations employed coded variables, with high and low levels designated as +1 and -1, respectively. This coding framework enables response prediction at defined factor levels and facilitates direct comparison of coefficients, thereby quantifying the relative influence of each parameter on the metal recovery and grade.
% Ni Recovery = + 15,00 - 0,6826A + 0,2264B + 0,6169C + 1,82D + 1,37AB - 1,22AC - 0,2715AD + 0,0446BC - 0,8591BD + 0,5839CD - 0,0664A² - 0,8203B² + 1,25C² +0,7903D² [
1]
% Ni Grade = + 0,3033 - 0,0032A + 0,0055B - 0,0165C - 0,0165D - 0,0222AB + 0,0150AC + 0,0241AD + 0,0020BC + 0,0174BD - 0,0128CD + 0,0153A² + 0,0096B² + 0,0003C² - 0,0022D² [
2]
% Cu Recovery = + 88,58 - 1,30A + 8,66B + 3,88C - 1,99D + 1,27AB - 6,60AC + 1,24AD + 6,22BC - 13,61BD - 4,75CD - 8,59A² - 10,61B² + 1,46C² - 2,79D² [
3]
% Cu Grade = + 0,2281 - 0,0196A + 0,0089B - 0,0281C - 0,0297D - 0,0363AB + 0,0205AC + 0,0247AD - 0,0103BC + 0,0259BD - 0,0249CD + 0,0073A² + 0,0159B² - 0,0101C² - 0,0028D² [
4]
% Zn Recovery = + 12,96 - 0,8455A - 7,16B + 1,01C + 0,9437D + 0,5978AB - 0,6425AC - 0,2726AD - 0,2396BC - 0,5824BD - 0,2061CD - 1,94A² + 8,85B² - 1,09C² - 1,29D² [
5]
% Zn Grade = + 0,0692 - 0,0032A - 0,0048B - 0,0003C - 0,0072D - 0,0101AB + 0,0083AC + 0,0042AD - 0,0031BC + 0,0048BD - 0,0093CD + 0,0007A² + 0,0075B² - 0,0029C² - 0,0036D² [
6]
% Pb Recovery = + 83,33 + 12,37A + 4,29B - 4,29C - 20,71D - 6,44AB - 6,06AC + 18,56AD + 6,06BC + 6,44BD + 6,06CD + 5,24A² + 5,24B² - 7,26C² - 7,26D² [
7]
% Pb Grade = + 0,0301 + 0,0015A + 0,0002B - 0,0011C - 0,0077D - 0,0078AB + 0,0086AC + 0,0016AD - 0,0040BC + 0,0079BD - 0,0022CD + 0,0022A² + 0,0015B² - 0,0025C² - 0,0029D² [
8]
The empirical model equations 1, 3, 5, and 7 described recoveries, while 2, 4, 6 and 8 addressed grade. Positive coefficients indicated that increasing a factor enhances recovery or grade, whereas negative coefficients denote a detrimental effect. For instance, a negative coefficient for collector dosage (A) in the nickel recovery model equation suggests excessive dosage reduces recovery, while a positive coefficient for flotation time reflects the benefit of extended flotation. Collectively, these model equations provide a predictive framework for optimising flotation by identifying how parameter adjustments influence both recovery and product quality.