“…Therefore, surface water treatment requires materials in which hardness and accessibility can be combined with flexibility and high number of active FGs in one “entity” with upgraded properties (high sorption capacity, fast kinetics, high selectivity, fast regeneration, and good reusability). These materials could be composite sorbents which fulfill the utility in fast targeting of different types of pollutants, such as heavy metal ions. − The control of FGs at a nanometric level and the creation of specific ligands onto composites (magnetic particles, membranes, carbon nanosheets, and hydrogels) for subsequent molecular interactions is essential in water purification, chromatography, controlled release of immobilized species, and so forth. − For some materials, high amounts of sorbed metal was reached at high equilibrium concentration in hundreds of minutes, in case of hydrogels and ionic resins where diffusion is a very important parameter of sorption. ,,, Other authors succeeded in decreasing the time of sorption by increasing the surface of the sorbent, in case of magnetic nanoparticles. , The inorganic/polyelectrolyte composites, with controlled architecture and chemical composition at nanometric level, can be obtained by: (i) polymerization of a monomer/colloidal particles mixture, (ii) polymer chains grafting onto/from solid surface, and (iii) deposition of thin films using monolayer or layer-by-layer (LbL) strategy. − LbL assembly, carried out mainly in aqueous environments, is an extensively used technique for engineering material surfaces and fabrication of LbL composite coatings. , The mechano-chemical stability of the composite multilayer under harsh/stress media is very important in sorption/separation of different pollutants (heavy metal ions, dyes, drugs, humic acids, etc.). Thus, thermal/chemical cross-linking of polymer chains on a composite surface must be carried out, either at the end or at each step of the LbL process .…”