Affiliations 

  • 1 Department of Civil and Environmental Engineering, The University of Auckland, New Zealand; Department of Environmental Engineering Technology, Universiti Kuala Lumpur - Malaysian Institute of Chemical and Bio-Engineering Technology, Malaysia
  • 2 Department of Environmental Engineering, Konkuk University, Republic of Korea
  • 3 School of Biological Sciences, The University of Auckland, New Zealand
  • 4 Ecole Nationale Supérieure de Chimie de Rennes, France
  • 5 Department of Civil and Environmental Engineering, The University of Auckland, New Zealand. Electronic address: n.singhal@auckland.ac.nz
Water Res, 2017 11 15;125:32-41.
PMID: 28826034 DOI: 10.1016/j.watres.2017.08.029

Abstract

The catalytic properties of nanoparticles (e.g., nano zero valent iron, nZVI) have been used to effectively treat a wide range of environmental contaminants. Emerging contaminants such as endocrine disrupting chemicals (EDCs) are susceptible to degradation by nanoparticles. Despite extensive investigations, questions remain on the transformation mechanism on the nZVI surface under different environmental conditions (redox and pH). Furthermore, in terms of the large-scale requirement for nanomaterials in field applications, the effect of polymer-stabilization used by commercial vendors on the above processes is unclear. To address these factors, we investigated the degradation of a model EDC, the steroidal estrogen 17α-ethinylestradiol (EE2), by commercially sourced nZVI at pH 3, 5 and 7 under different oxygen conditions. Following the use of radical scavengers, an assessment of the EE2 transformation products shows that under nitrogen purging direct reduction of EE2 by nZVI occurred at all pHs. The radicals transforming EE2 in the absence of purging and upon air purging were similar for a given pH, but the dominant radical varied with pH. Upon air purging, EE2 was transformed by the same radical species as the non-purged system at the same respective pH, but the degradation rate was lower with more oxygen - most likely due to faster nZVI oxidation upon aeration, coupled with radical scavenging. The dominant radicals were OH at pH 3 and O2- at pH 5, and while neither radical was involved at pH 7, no conclusive inferences could be made on the actual radical involved at pH 7. Similar transformation products were observed without purging and upon air purging.

* Title and MeSH Headings from MEDLINE®/PubMed®, a database of the U.S. National Library of Medicine.