Due to high permeability of soil and low absorption of radionuclides to soil particles enhance the losses rate of these radionuclides. The uptake of radionuclides by plants increases with the low radionuclide adsorption capacity to soil particles. Additionally, the behavior of radionuclides in soil depends on different biochemical processes (e.g., decomposition of organic matter changes soil property from an oxidizing to as a reducing medium). That’ reason the uptake of radionuclides from soil-to-plant is usually affected by many factors such as, physico-chemical form of radionuclide, plant species, internal translocation mechanisms within the plant, soil characteristics (pH value), isotopic-binding mechanism of soil, fertilizers (potassium or calcium nitrates, phosphate, organic), chelating agents (organic compounds), distribution of radionuclides in soil and environmental conditions [Martinez-Aguirre & Perianez, 1998; Foth,1978; Abdulaziz Alharbi & A. El-Taher, …show more content…
In Table 6, the radio-element concentrations of 226Ra, 232Th and 40K in soil samples varied from 0.647 to 1.765 ppm, 1.301 to 4.572 ppm and 0.611 to 2.262 %, respectively. The mean value of radio-element concentrations of 226Ra, 232Th and 40K were 1.020 ± 0.187 ppm, 2.533 ± 0.521 ppm and 1.050 ± 0.279 %, respectively. As low values of radio-elements concentrations of 226Ra and 232Th in soil samples might be explained the less contents of silicon dioxide (SiO2) and mafic minerals (Mavi and Akkurt, 2010; Damla, et al., 2012) whereas high values of radioelement concentrations of 40K may be due to high contents of light minerals (potash-feldspar and