Due to their tuneable surface properties, engineered nanoparticles are widely used in various consumer products, industries, and biomedical fields (Grillo et al., 2015;Kessler, 2011;Rudramurthy & Swamy, 2018). This results in their inevitable release into wastewater. Traditional municipal wastewater treatment plants are not capable of removing engineered nanoparticles (Chauque et al., 2014;Khan et al., 2021). Hence, engineered nanoparticles, along with active bio-nanoparticles, such as viruses, may enter the subsurface through land application of treated wastewater, and wastewater disposal to surface water bodies, and eventually enter the subsurface. Before reaching groundwater, they get transported through the vadose zone, where a fraction of the infiltrated particles is retained at grain surfaces (also called solid-water interface, SWI), air-water interface (AWI), and air-water-solid (AWS) contact region (