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Like in these studies for fruit vegetables remarkable differences between the heavy metals contents of rural areas (non contaminated areas), semi-urban and industrial areas [10, 25] were observed.
Similar agrochemical characteristics of the soils in areas contaminated with heavy metals (pH, humus and clay) as well as the high heavy metals contents of these soils, account for the similarity in their make their translocation in plants.
This model was computed also only with heavy metals contents of vegetables and its PC1 and PC2 biplot is presented in Figure 5. Figure 5 Biplot of PC1 and PC2 for vegetables data grouped on vegetables species, used PCA3-plant model.
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The order of leachable heavy metals' content of the vermicompost was: Fe > Mn > Ni > Zn > Cr > Pb > Cu > Cd.
The metals content of the sorbed complexes are eluted using 4.0 mL of 1.0 mol L-1 nitric acid.
Soil type is one of the most important factors to determine the metals' content of food plants (Itanna 2002; Roy et al. 2007).
The metal contents of the purified SOD1 proteins that were metalated in vivo and used in this study as they were isolated ("as isolated" proteins) are presented in Table 1.
The analysis revealed that the metal contents of the catalyst was close (±0.4%) to the target metal content of 75 wt% Fe.
The data of CHN and metal contents of the complexes are presented in Table 3.
The heavy metal contents of Evernia prunastri samples were determined by atomic absorption spectrometry.
This table shows that the metal contents of the catalysts were fairly similar and close to the targeted metal contents.
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