Sorption of selected pharmaceuticals by a river sediment: role and mechanisms of sediment or Aldrich humic substances.

Environ Sci Pollut Res Int

UMR IC2MP 7285, CNRS/Université de Poitiers, ENSIP, TSA 41105, 1 rue Marcel Doré, 86073, Poitiers, Cedex 9, France.

Published: May 2018

AI Article Synopsis

  • The study compares the effects of humic substances (HS) from river sediment and from Aldrich on the sorption of selected pharmaceuticals (SMX, DCF, TMP, ATN) onto river sediment.
  • While river HS generally increased the sorption of SMX, DCF, and TMP, it decreased ATN sorption; Aldrich HS had the opposite effect for SMX and DCF but increased TMP and ATN sorption.
  • The research findings suggest that the sorption mechanisms are multilayered and not solely dependent on HS types, with river HS binding to sediments and Aldrich HS potentially releasing compounds into solution.

Article Abstract

Sorption of pharmaceuticals onto sediments is frequently related to organic matter content. Thus, the present work aimed to compare the effect of humic substances (HS) extracted from a river sediment versus Aldrich (HS) on the sorption of selected pharmaceuticals onto this river sediment. The results exhibited no "unique" effect of the presence of HS from the same origin. Thus, the sediment HS increased the sorption of sulfamethoxazole (SMX), diclofenac (DCF), and trimethoprim (TMP), but reduced the sorption of atenolol (ATN). The presence of Aldrich HS increased the sorption of TMP and ATN and decreased the sorption of SMX and DCF. Fluorescence quenching measurements revealed that these effects cannot be explained only by the presence of pharmaceutical HS associations. The use of several sorption models suggested that the sorption of SMX, DCF, and ATN involves multilayer mechanisms. Furthermore, it was pointed out that the presence of HS does not change the sorption mechanisms although it was observed interaction between HS and the sediment. Indeed, the sediment HS sorbs onto the sediment whereas the Aldrich HS tends to mobilize organic compounds from the sediment to the solution.

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Source
http://dx.doi.org/10.1007/s11356-018-1684-0DOI Listing

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