2014
DOI: 10.1016/j.scitotenv.2013.11.036
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Sorption/desorption of non-hydrophobic and ionisable pharmaceutical and personal care products from reclaimed water onto/from a natural sediment

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Cited by 125 publications
(57 citation statements)
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“…Besides this, sorption onto suspended particulate matter or sediments can occur. High distribution coefficients (k d ) were observed in other studies for CAF (17.9-250 L kg −1 ), ATN (8.1 L kg −1 ), and NPX (1.9 L kg −1 ), although for PAR sorption is reported to be negligible (k d 0.5-2.8 L kg −1 ) (Lin et al 2010;Martínez-Hernández et al 2014;Yamamoto et al 2009). …”
Section: Spatiotemporal Distributionmentioning
confidence: 73%
“…Besides this, sorption onto suspended particulate matter or sediments can occur. High distribution coefficients (k d ) were observed in other studies for CAF (17.9-250 L kg −1 ), ATN (8.1 L kg −1 ), and NPX (1.9 L kg −1 ), although for PAR sorption is reported to be negligible (k d 0.5-2.8 L kg −1 ) (Lin et al 2010;Martínez-Hernández et al 2014;Yamamoto et al 2009). …”
Section: Spatiotemporal Distributionmentioning
confidence: 73%
“…The main suggested sorption mechanisms of atenolol in the literature are electrochemical interaction and ion exchange [29,41,49,50] and could be via charge transfer interaction due to the structure of the molecule, with its electron donor atoms (two nitrogen atoms and one oxygen form OH group) or hydrogen bonding interaction [49,56]. Schaffer et al [41] found that 99% of the total sorption of atenolol was by cation exchange interaction.…”
Section: Suggested Mechanisms Of Interactionmentioning
confidence: 99%
“…the octanol-water partitioning coefficients (Kow)), the sorption of pharmaceuticals, which are typically ionisable compounds, to environmental solids is thought to be through a combination of interactions e.g. hydrogen bonds, electrostatic interactions, ionic exchange and hydrophobic interactions [26][27][28][29][30]. Moreover, while the organic carbon content (OC) of sediments is known to be important in explaining the differences in the sorption behaviour of a neutral organic chemical across different soil or sediment types, factors such as the solid phase component (clay and metal content), surface exchangeable cations and pH probably play an important role in determining sorption of ionisable compounds [30][31][32].…”
Section: Introductionmentioning
confidence: 99%
“…The ultimate fate of organic micropollutants in the aquatic environment is a current environmental issue (Loffler et al 2005;Shareef et al 2006;Styszko et al 2010;Caldwell et al 2014;Martínez-Hernández et al 2014). Sorption of organic micropollutants is determined by different factors: the chemical nature of micropollutants, the ionization state, water solubility, the properties of the sorbent and temperature.…”
Section: Introductionmentioning
confidence: 99%