Fate of Sulfamethoxazole, 4-Nonylphenol, and 17β-Estradiol in Groundwater Contaminated by Wastewater Treatment Plant Effluent

Larry B. Barber*, Steffanie H. Keefe, Denis R. LeBlanc, Paul M. Bradley§, Francis H. Chapelle§, Michael T. Meyer, Keith A. Loftin, Dana W. Kolpin and Fernando Rubio#
U.S. Geological Survey, 3215 Marine Street, Boulder, Colorado 80303, U.S. Geological Survey, 10 Bearfoot Road, Northborough, Massachusetts 01532, U.S. Geological Survey, 720 Gracern Road, Suite 129, Columbia, South Carolina 29210, U.S. Geological Survey, 4821 Quail Crest Place, Lawrence, Kansas 66049, U.S. Geological Survey, 400 South Clinton Street, Iowa City, Iowa 52244, and Abraxis, 54 Steamwhistle, Warminster, Pennsylvania 18974
Environ. Sci. Technol., 2009, 43 (13), pp 4843–4850
DOI: 10.1021/es803292v
Publication Date (Web): May 20, 2009
Copyright © 2009 American Chemical Society
* Corresponding author e-mail: lbbarber@usgs.gov; phone: 303-541-3039., †

U.S. Geological Survey, Boulder, CO.

, ‡

U.S. Geological Survey, Northborough, MA.

, §

U.S. Geological Survey, Columbia, SC.

,

U.S. Geological Survey, Lawrence, KS.

,

U.S. Geological Survey, Iowa City, IA.

, #

Abraxis, Warminster, PA.

Abstract

Organic wastewater contaminants (OWCs) were measured in samples collected from monitoring wells located along a 4.5-km transect of a plume of groundwater contaminated by 60 years of continuous rapid infiltration disposal of wastewater treatment plant effluent. Fifteen percent of the 212 OWCs analyzed were detected, including the antibiotic sulfamethoxazole (SX), the nonionic surfactant degradation product 4-nonylphenol (NP), the solvent tetrachloroethene (PCE), and the disinfectant 1,4-dichlorobenzene (DCB). Comparison of the 2005 sampling results to data collected from the same wells in 1985 indicates that PCE and DCB are transported more rapidly in the aquifer than NP, consistent with predictions based on compound hydrophobicity. Natural gradient in situ tracer experiments were conducted to evaluate the subsurface behavior of SX, NP, and the female sex hormone 17β-estradiol (E2) in two oxic zones in the aquifer: (1) a downgradient transition zone at the interface between the contamination plume and the overlying uncontaminated groundwater and (2) a contaminated zone located beneath the infiltration beds, which have not been loaded for 10 years. In both zones, breakthrough curves for the conservative tracer bromide (Br) and SX were nearly coincident, whereas NP and E2 were retarded relative to Br and showed mass loss. Retardation was greater in the contaminated zone than in the transition zone. Attenuation of NP and E2 in the aquifer was attributed to biotransformation, and oxic laboratory microcosm experiments using sediments from the transition and contaminated zones show that uniform-ring-labeled 14C 4-normal-NP was biodegraded more rapidly (30−60% recovered as 14CO2 in 13 days) than 4-14C E2 (20−90% recovered as 14CO2 in 54 days). There was little difference in mineralization potential between sites.

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History

  • Published In Issue July 01, 2009
  • Article ASAPMay 20, 2009
  • Received: November 20, 2008
    Revised: March 19, 2009
    Accepted: March 30, 2009

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