... Table 1 presents both measured and estimated degrees of removal for selected EDCs/PPCPs in WW treatment plants under dry-weather circumstances, using representative samples of the current literature concerning biodegradability, along with tendencies regarding sorption to sludge and oxidation by chlorination/ozonation. Numerous prior researches have reported that EDCs/PPCPs are eliminated to various levels by both conventional and advanced treatment techniques such as coagulation/flocculation (Westerhoff et al., 2005;Joseph et al., 2012;Jung et al., 2015), chlorination (Westerhoff et al., 2009), activated carbon Snyder et al., 2007;Jung et al., 2013), carbon nanoparticles (e.g., carbon nanotubes (Joseph et al., 2011a;Joseph et al., 2011b;Zaib et al., 2012) and graphene oxides (Nam et al., 2015)), metal-organic frameworks (Jun et al., 2019a;Jun et al., 2020b), MXenes (Jun et al., 2019b;Jun et al., 2020a), membrane (Yoon et al., 2006Heo et al., 2013), O 3 (Westerhoff et al., 2005;Moreira et al., 2015), ultraviolet (UV) radiation Farzadkia et al., 2014;Duan et al., 2017), sonodegradation (Rahimi et al., 2016;Rao et al., 2016;Serna-Galvis et al., 2016), non-thermal plasma (NTP) (Ansari et al., 2020), and biodegradation (Yoon et al., 2010;Ryu et al., 2011Ryu et al., , 2014. Unlike commonly recognized advanced oxidation methods such as O 3 /H 2 O 2 , UV/TiO 2 , UV/H 2 O 2 , and UV/Fe 3+ /H 2 O 2 processes, the NTP process has lately been employed as an advanced treatment method for the elimination of complicated organic chemicals in water and WW (Gerrity et al., 2010;Ceriani et al., 2018;Feng et al., 2018;Fan et al., 2021). ...