As shown in Figure 4, comparatively to the other responses, lower R and R adjusted characterize the 2nd-round models obtained for NPQ800 (this difference was also noticed in the 1st-round models; see Table 3).
A lower incidence of dysuria, assessed by the Boyarsky scale (Table 3), was noticed in the treatment group, with symptoms being generally milder than in the control group.
As can be noticed in Table 4, the value of the exponent ns is very close to unity (0.9, 0.9, and 0.99 for 2,4 dinitrophenol, 2 nitrophenol, and 4 nitrophenol, respectively), which explains the values of qm obtained from this model.
As can be noticed in Table 4, the relative abundances inferred from the analysis of the emission spectrum fit fairly well the values expected from chondritic materials.
As can be noticed in Table 4, the average value of 239+240Pu in the soil is about 200 mBq/kg; the concentration of plutonium in lake sediments exceeds this value by 10 times; however, in river sediments it is about 4 times lower.
As can be noticed in Table 8, the experimental Q e values are so distant from the calculated ones and the correlation coefficients are low, suggesting that this adsorption does not obey a pseudo-first kinetic model; the graphs in Fig. 19 are not straight lines, precluding the validity of Lagergren equation.
As can be noticed in Table 2, the range of parameters is a bit larger in this test than in the previous one.
As noticed in Table 4, the time needed to transfer a bit-stream to hardware using the PCAP interface depends on the size of the partial bit-stream file.
As an interesting point to be noticed in Table 3, the eleventh and twelfth tests have a good result in AUC curve, which are 0.859 and 0.839 in success rate and 0.858 and 0.839 in predictive rate respectively.
As noticed in Table 2, the new EPSTRA methods achieved better results than existing automatic approaches, almost reaching the performance of human experts.
