Cytarabine (CY) is an anticancer drug which has been identified in wastewater influents, effluents, and surface waters. In the present study, the degradation of CYunder simulated solar light (SSL), by photo-Fenton (Fe 3+ /H 2 O 2 /SSL) and photo-Fenton-like processes (Fe 3+ /S 2 O 8 2− /SSL and [Fe(C 2 O 4 ) 3 ] 3− /H 2 O 2 /SSL), was investigated. The major parameters affecting the applied treatments (e.g., concentration of CY, Fe 3+ , H 2 O 2 , and S 2 O 8 2−) were optimized and CY's complete removal was achieved within 45 min for all techniques used. Mineralization studies indicated that [Fe(C 2 O 4 ) 3 ] 3− /H 2 O 2 /SSL treatment was the most efficient procedure since faster kinetics are achieved and higher mineralization percentage is reached compared to the other techniques used. Furthermore, 12 transformation products (TPs) were identified during the applied processes, by high resolution mass spectrometry, four of which were identified for the first time, indicating that CY molecule undergoes hydroxylation and subsequent oxidation, during the applied processes. Moreover, predictions of acute and chronic ecotoxicity of CY and its TPs on fish, daphnia, and green algae were conducted, using in silico quantitative structure activity relationship (QSAR) calculations. According to these predictions, the TPs generated during the studied treatments may pose a threat to aquatic environment. Finally, the efficiency of CY degradation by photo-Fenton and photo-Fenton-like treatment in real wastewater was evaluated, under the optimized conditions, which resulted in lower degradation rate constants compared to ultrapure water.