within the dense polymer separation layer. TFNs are therefore known for producing high liquid permeance and used for reverse osmosis and nanofiltration [13-16] and organic solvent nanofiltration. [10] As an example, zeolite-polyamide TFN membranes are used for reverse osmosis, [9,17-19] where a radical increase of ≈80% in water permeance along with a comparable solute rejection is reported. [9] Other porous and nonporous nanostructure [19,20] , zeolite imidazole framework (ZIF-8), [21] TiO 2 nanoparticles, [22,23] CeO 2 nanoparticles, [24] carbon dots, [25] graphene oxide, [26-30] silica nanoparticles, [31] and multi-walled carbon nanotubes (MWCNTs), [32] have been incorporated in the separation layer to study water permeance and salt rejection behavior of TFN membranes. Additionally, the incorporated nanoparticles in the polyamide membranes are also known for their antimicrobial and antibacterial properties. [9,20] The addition of zeolite nanoparticles in the separation layer formed more permeable, negatively charged, and thicker polyamide films. [19] Smaller zeolites produced greater permeability enhancements, but larger zeolites produced more favorable surface properties in designing thin-film nanocomposite reverse osmosis membranes. [19] However, no microscopic study for thicker polyamide layer which produces more water flux is reported. As a significant reduction in salt rejection is observed, the creation of defects in the separation layer is expected. Carboxy-functionalized multiwalled carbon nanotubes (MWNTs) incorporated membranes also show an increase in water flux with a somewhat decrease in salt rejection. [32] The fabrication of TFNs often follows the process of inclusion of nanomaterials in the separation layer by dispersing them in the aqueous [33-35] or the organic phase [10,19,33,36,37] during interfacial polymerization. However, the surface property of the nanomaterials would restrict their dispersion either in aqueous or in the organic phase. Generally speaking, the hydrophilic nanomaterials are favorable for aqueous dispersion [11] and the hydrophobic nanomaterials are promising for dispersion in the organic phase. [38] Still, there are problems of incorporating hydrophilic nanomaterials by dispersing them in the organic phase as they may get precipitated during interfacial polymerization. [39] A study by Xue and his co-workers used hollow zwitterionic nanoparticles and non-hollow nanoparticles in the separation layer by dispersing The role of the nanostructured materials incorporated in the separation layer of thin-film composite membranes is not properly understood yet, as it requires stringent salt rejection values, proper imaging of the separation layer to realize the presence of nanostructured materials, and to know the thickness of the separation layer. Here, the scalable fabrication of high flux positively charged "polyamide composite nanofiltration" membranes with an ultrathin nanofilm separation layer of ≈14 nm produced via interfacial polymerization of polyethyleneimine and trimesoyl...