Photolysis
Hydroxyl radicals
Kinetics
ByproductDegradation mechanism a b s t r a c tThe degradation of four pharmaceutical compounds (PhACs), ibuprofen (IBU), diphenhydramine (DP), phenazone (PZ), and phenytoin (PHT) was investigated via ultraviolet (UV) photolysis and UV/H 2 O 2 process with a low-pressure (LP) UV lamp. For each PhAC tested, direct photolysis quantum yields at 254 nm were found to be ranging from 6.32 Â 10 À2 to 2.79 Â 10 À1 mol E À1 at pH 7. The second-order rate constants of the reaction between the PhACs and OH were determined to be from 4.86 Â 10 9 to 6.67 Â 10 9 M À1 s À1 by using a competition kinetic model which utilized para-chlorobenzoic acid ( pCBA) as a reference
IntroductionPharmaceutical compounds (PhACs) are developed and manufactured for specific biological effects, to improve human and animal health care, and livestock farming. PhACs are continuously introduced into the environment and are prevalent at small concentrations (Kolpin et al., 2002), which can affect water quality and potentially impact drinking water supplies, ecosystem and human health (Heberer, 2002b;Roefer et al., 2000;Trussell, 2001). Some of the adverse effects caused by pharmaceutical pollution include aquatic toxicity, resistant development in pathogenic bacteria, genotoxicity, and endocrine disruption (Halling-Sørensen et al., 1998;Kü mmerer, 2004;Sumpter, 1998). The presence of trace pharmaceutical and other xenobiotic compounds in finished drinking water is another public health concern, since little is known about potential chronic health effects associated with long term ingestion of mixtures of these compounds through drinking water (Kü mmerer, 2001;Stackelberg et al., 2004). Thus, it is an emerging issue in environmental science and * Corresponding author. Tel.: þ86 10 62849628; fax: þ86 10 62923541. E-mail address: huchun@rcees.ac.cn (C. Hu).A v a i l a b l e a t w w w . s c i e n c e d i r e c t . w a t e r r e s e a r c h 4 3 ( 2 0 0 9 ) 1 7 6 6 -1 7 7 4