“…The dissolution of Fe(III) plays an significant role in the cycling of Fe in aquatic systems, and iron release kinetics can be controlled by many environmental factor, including particle size (Madden, Hochella, & Luxton, 2006), pH, sunlight intensity (Song et al, 2005), oxygen, organic ligands and the incorporation with other metal ions (Alvarez, Sileo, & Rueda, 2008). Organic ligands common in water are formate, acetate, citrate and oxalate (Graedel, Mandich, & Weschler, 1986;Zuo & Hoigne, 1992), and among them, oxalate was the most effective ligand (Panias, Taxiarchou, Douni, Paspaliaris, & Kontopoulos, 1996), and it could affect iron dissolution kinetics significantly. Mobility of iron in aquatic environments can be enhanced by (1) proton-promoted dissolution that leads metal-oxygen bonds to be loosened, thus lead to iron release (Xu & Gao, 2008), (2) ligand-promoted dissolution that forms soluble Fe(III) complexes with ligands (Wang, Schenkeveld, Kraemer, & Giammar, 2015) and (3) reduction of Fe(III) to the more soluble form of Fe (II) under anoxic environment or with the presence of reductive solution (Dos Santos Afonso, Morando, Blesa, Banwart, & Stumm, 1990) It has been reported that trace metal dopant could affect iron oxide structure and properties markedly including surface specific area, particle size (Mohapatra, Anand, Das, Upadhyay, & Verma, 2002;Warner et al, 2012), crystallization (H. Ebinger & G. Schulze, 1989), zeta potential (Alvarez et al, 2015) and adsorption behavior towards phosphate (Li et al, 2016) and metal ions (Rout et al, 2014).…”