h i g h l i g h t s• Climbazole (CZ) could be effectively degraded under UV-254 irradiation.• CZ underwent direct and selfsensitized photolysis involving ROS.• The main photodegradation byproducts of CZ were identified and semi-quantitated.• Pathway includes hydroxylative dechlorination, dechlorination, and de-pinacolone.• The toxicity of the photodegradation system reduced after UV-254 irradiation. Keywords: Climbazole Photodegradation Reactive oxygen species By-products Toxicity a b s t r a c t Climbazole (CZ) has been known to persist in various environmental media, and may cause potential risks to aquatic organisms. This study investigated the photodegradation of CZ by ultraviolet (UV, 254 nm) under different conditions. The results revealed that CZ could be effectively degraded in aqueous solutions under UV-254 irradiation with a half-life of 9.78 min (pH = 7.5), and the photodegradation followed pseudo-first-order kinetics. pH had almost no effect on its rate constants and quantum yields; but the water quality of natural waters could affect the photolysis of CZ, and the coexisting constituents such as Fe 3+ , NO 3 − , and HA obviously inhibited its photolysis. The addition of different radical scavengers also inhibited the photodegradation of CZ due to the reduction of reactive oxygen species (ROS). CZ underwent direct and self-sensitized photolysis involving ROS. Based on the identified photodegradation by-products, the proposed pathways included hydroxylative dechlorination, dechlorination and de-pinacolone. Moreover, toxicity evaluation using duckweed found significant toxicity reduction in the photodegradation system of CZ after the irradiation of UV-254, and the remaining by-products did not pose extra toxicity compared with CZ itself. These findings from present study suggest that CZ in effluent could be further reduced by applying UV photolysis treatment.