International Journal of Environmental Research, cilt.20, sa.6, ss.1-25, 2026 (Hakemli Dergi)
Metolachlor is one of the most frequently detected herbicides in drinking water sources, posing a significant environmental
risk. In this study, an L-arginine functionalized magnetic Fe₃O₄/activated carbon nanocomposite (Fe₃O₄/L-Arg@AC) was
synthesized and its metolachlor removal performance was evaluated. The kinetic and equilibrium adsorption mechanisms
of Fe₃O₄/L-Arg@AC for metolachlor removal were investigated comparatively with pure activated carbon (AC-Puriss),
nitric acid modified activated carbon (AC-HNO₃), and Fe₃O₄/L-Arg. Although Fe₃O₄-based, L-arginine functionalized, and
activated carbon-containing systems have been studied in the literature for different pollutants, the use of Fe₃O₄/L-Arg@
AC composite for metolachlor removal is limited. FTIR analyses confirmed successful binding of L-arginine functional
groups to the surface, while SEM images revealed that the composite exhibited a more homogeneous distribution and an
improved porous surface morphology. Kinetic analyses showed that adsorption process was not limited to diffusion alone
but was based on a multi-stage mechanism where liquid film and intraparticle diffusion processes acted together. The
functionalized structure exhibited faster mass transfer and more efficient adsorption behavior compared to Fe₃O₄/L-Arg.
Equilibrium data indicated that Freundlich model was more suitable for the composite structure and that heterogeneous
surface properties were dominant. Metolachlor adsorption capacity remained stable under neutral and slightly basic pH
conditions, while it was only minimally affected under acidic conditions. In addition, the synthesized adsorbent exhibited
good reusability with a regeneration efficiency of 93.2% over five consecutive adsorption-desorption cycles. This study
demonstrated the Fe₃O₄/L-Arg@AC composite as an effective, reusable, functional, and viable adsorbent alternative for
metolachlor removal in practical water treatment systems.