“…However, many of the studies were without application of any kinetic models and were based on just showing the variation in adsorption capacity with time and usually to establish the time taken to arrive at equilibrium. A cross-section of such works that considered adsorption on various inorganic solids without dealing with any of the kinetic aspects is given below: Cu(II) on Ca-kaolinite [64], Cd(II), Cu(II) and Pb(II) on diatomite and Mn-diatomite [65], Ca(II) on hydroxy-Al pillared montmorillonite [66], Cd(II), Cr(III), Cu(II), Ni(II), Pb(II) and Zn(II) on kaolinite and illite [67], Cu(II) on sewage sludge ash [68], Ni on illite [69], Cd(II), Cr(III), Cu(II), Mn(II), Ni(II), Pb(II) and Zn(II) on Na-montmorillonite [70], As(V) on calcined synthetic hydrotalcite and calcined natural boehmite [71], Cd(II) and Zn(II) on apatite [72], Co(II), Cu(II), Mn(II) and Zn(II) on natural zeolite [73], Cu(II), Pb(II) and Zn(II) on natural zeolite [74], As(V) on bimetal oxide [75], Cd(II) and Pb(II) on amine-modified zeolite [76], As(III) and As(V) on TiO 2 [77], Cd(II) and Zn(II) on modified clinoptilolite [78], Co(II) and Zn(II) on treated bentonite [79], Cu(II) on clinoptilolite [80], Cu(II), Co(II) and Zn(II) on natural bentonite [81], Cr(III) on zeolite [82], Cr(VI) on surfactant-modified zeolite [83], Co(II) and Ni(II) on ion exchange resins [84], Hg(II) on natural and modified montmorillonite (treated with pyridine, dimethyl sulfoxide and 3-aminopropyltriethoxysilane) [85], Cd(II), Cr(III) and Mn(II) on natural sepiolite [86], Cu(II) on Serbian zeolite, clay and diatomite [87], Cu(II) on bentonite-polyacrylamide composites [88], etc.…”