Introduction Nanoparticles (NPs) from natural and anthropogenic sources can appear in the soil (Morales-Díaz et al., 2017; Kumar et al., 2019). Nowadays, NPs have been widely used in various products and industries, however, their release into the environment threatens living organisms (Zafar et al., 2016). Entry and toxicity concerning NPs to plants rely on the chemical construction and size that impacts the ligand-receptor interactions (Raliya et al., 2016). ZnO NPs are significantly used in various products as well as in the agriculture and food sector, like pesticides, fungicides, and fertilizers (Ghosh et al., 2016 ; Housseiny & Gomaa, 2019). The toxic impact of NPs has been reported as a result of size, morphology, nature, composition, reactivity, and other NPs capacities (Zaka et al.,