“…It is known that the electro-chemical oxidation of organic contaminants comprises two mechanisms: (i) direct oxidation occurring at the anode surface by the chemisorbed •OH (E 0 = 2.8V), when an active electrode is used (similar to the one used here), and (ii) indirect oxidation through the generation of a mediator in the bulk solution (like active chlorine). The differences observed in the decay levels of the recalcitrant CECs might be explained by their structural differences [47], and/or distinct physicochemical properties (ESI 1). For example, in the 4-aminosalicylic acid the presence of a -NH 2 group in metaposition to -OH and para-position to -COOH slightly activated the electrophilic attack of •OH, compared to the salicylic acid without any -NH 2 group, in water samples using a boron doped diamond/air-diffusion cell [47].…”