UV/persulfate (UV/PS) is considered an effective process for the degradation of emerging micropollutants in aquatic media. However, under the influence of complex water matrices such as wastewaters, radicals created during UV/PS will be reduced and transformed, so the chemical process of effectively obtaining the radicals in the system is very important to improving degradation efficiency. Thus, in the study, neotame (NEO, an artificial sweetener), as an emerging contaminant, was selected as the target compound to investigate in terms of its degradation and the role of free radicals in a range of water matrices during the UV/PS process. Based on the low concentration probe method (probe concentration <= 0.2 mu m, more than 3-fold improvement in radical detection accuracy), kinetic modeling was developed to determine the role of primary (center dot OH and SO4 center dot-) and secondary ( e.g. Cl center dot, Cl2- center dot, CO3 center dot-, and NO3 center dot) radicals. Results indicated that UV/PS was effective in decomposing NEO (>93.7 %) within 7 min and was mainly attributed to center dot OH and SO4 center dot-.Acidic environments promote NEO degradation with a greater contribution from SO4 center dot-.Natural organic matter inhibited NEO degradation by quenching radicals (especially center dot OH). The k obs of NEO degradation in the presence of Cl-remained almost unchanged due to the production of Cl center dot and Cl-2-center dot compensating the depletion of SO4 center dot-. The presence of HCO3- quenched a part of primary radicals, which led to a decrease in k obs of NEO degradation, but CO3 center dot- began to play a partial degradation role. In the presence of NO3- , UV-activated production of center dot OH and NO2 center dot promoted NEO degradation. Based on 39 transformation products obtained, 3 degradation pathways and 7 radical attack ways were proposed for NEO degradation by primary and secondary radicals in the UV/PS system. This study provides meaningful insight into the role of primary and secondary radicals in NEO degradation using UV/PS systems.