251-2 Interactions of Pharmaceutical Compounds with Dissolved Organic Matter (DOM).

See more from this Division: S11 Soils & Environmental Quality
See more from this Session: Reuse of Wastewaters: Fate and Effects of Emerging Contaminants: II/Div. S11 Business Meeting
Tuesday, November 2, 2010: 1:15 PM
Hyatt Regency Long Beach, Seaview Ballroom C, First Floor
Share |

Benny Chefetz, Adi Maoz and Rotem Navon, Hebrew University of Jerusalem, Rehovot, Israel

Pharmaceutical compounds and dissolved organic matter (DOM) are co-introduced into the environment by irrigation with reclaimed wastewater and/or application of biosolids. In this study, we evaluate the role and mechanism of interaction of the pharmaceuticals naproxen and carbamazepine with structural fractions of biosolids-derived DOM. Sorption interactions were estimated from dialysis-bag experiments at different pHs with six structural fractions of DOM.

Binding of naproxen and carbamazepine by the hydrophobic acid fraction (HoA) exhibited strong pH-dependence. With both pharmaceuticals, the highest binding coefficients (KDOC) were at pH 4. With the hydrophobic neutral fraction (HoN), pH affected only naproxen binding (decreasing with increasing pH). Among the hydrophilic DOM fractions, the hydrophilic acid fraction (HiA) exhibited the highest KDOC value for carbamazepine, probably due to their bipolar character. In the hydrophilic acid fraction-naproxen system, significant anionic repulsion was observed with increasing pH. The hydrophilic base fraction (HiB) contains positively charged functional groups. Therefore with increasing ionization of naproxen (with increasing pH), KDOC to this fraction increased. The hydrophilic neutral fraction (HiN) exhibited the lowest KDOC with both studied pharmaceuticals.

The KDOC value of carbamazepine with the bulk DOM sample was higher than the calculated KDOC value based on binding by the individual isolated fractions. The opposite trend was observed with naproxen at pH 8: the calculated KDOC value was higher than the value obtained for the bulk DOM. These results demonstrate that DOM fractions interact with each other and do not act as separate sorption domains. This study also demonstrates that the binding abilities of the DOM fractions can also significantly affect the mobility of pharmaceutical compounds in soils influenced by intensive irrigation with reclaimed wastewater or amended with biosolids.

See more from this Division: S11 Soils & Environmental Quality
See more from this Session: Reuse of Wastewaters: Fate and Effects of Emerging Contaminants: II/Div. S11 Business Meeting