Fe–Mn Biochar Composites from Sugarcane Bagasse for Herbicides Removal: Structure, Mechanisms, and Safety Relationships toward Sustainable Water Treatment

High Resolution Image Download MS PowerPoint Slide Fe–Mn biochar composites were synthesized from sugarcane bagasse through prepyrolytic impregnation with FeCl 3 and MnCl 2, using immersion (IME) and coprecipitation (COP) methods, followed by pyrolysis at 600 °C for 2 h. Their characterization revealed distinct differences in surface chemistry and oxide dispersion. Both composites contained mixed Fe 3 O 4, Fe 2 O 3, MnO, and Mn 3 O 4 phases, but IME exhibited a amorphous carbon matrix, while COP displayed greater crystallinity (∼41%). In aqueous adsorption studies, IME maintained nearly constant removal efficiency across pH 2–10, whereas COP was strongly pH-dependent, leading to IME’s selection for subsequent studies. Adsorption isotherms of 2,4-dichlorophenoxyacetic acid (2,4-D) and picloram (25 °C; 2 g L –1 ) were well fitted by the Sips model, with maximum adsorption capacities of 18.1 and 8.1 mg g –1, respectively. X-ray photoelectron spectroscopy of IME revealed Fe 3+ /Fe 2+ and Mn 3+ /Mn 2+ species and indicated that 2,4-D removal occurred mainly by Fe 3+ -carboxylate complexation, while picloram adsorption involved weaker polar and van der Waals interactions. Reuse tests showed a decline in performance after three cycles (∼97% → 29%), suggesting active-site blockage. Metal leaching from IME at pH 5 was limited (0.025 mg L –1 for Fe and 2.94 mg L –1 for Mn). Fe complied with drinking-water limits, whereas Mn exceeded them, highlighting the need for safety evaluation. Phytotoxicity assays using Cucumis sativus confirmed no adverse effects from residual 2,4-D, demonstrating effective detoxification. Overall, Fe–Mn biochar composites present a promising, sustainable approach for herbicide removal, but the environmental safety of treated effluents should be ensured.