Published September 2018 | Version v1
Journal article

Seasonal variations of steroid hormones released by wastewater treatment plants to river water and sediments: Distribution between particulate and dissolved phases

  • 1. Civil, Geological and Mining Engineering Department, Polytechnique de Montréal, CP 6079, succ. Centre-Ville, Montréal, QC H3C 3A7 (Canada)
  • 2. Department of Chemistry, Université de Montréal, P.O. Box 6128, succ, Centre-Ville, Montréal, QC H3C 3J7 (Canada)
  • 3. Canada Research Chair in Microbial Contaminant Dynamics in Source Waters, Civil, Geological and Mining Engineering Department, Polytechnique de Montréal, QC (Canada)
  • 4. NSERC Industrial Chair on Drinking Water, Civil, Geological and Mining Engineering Department, Polytechnique de Montréal, QC (Canada)

Description

Highlights: • Environmental levels of steroids were determined in dissolved and particulate phases. • Extensive amounts of steroids detected in suspended particles and sediment. • Steroids in drinking water intakes were at the same level as treated sewage. • Biological refractory steroids may accumulate in drinking water plant sludge. Extensive environmental monitoring was conducted in an urban river impacted by multiple combined sewer overflows (CSOs) and wastewater treatment plant (WWTP) discharge points. Temporal and spatial distributions of dissolved and particulate steroids (progesterone (Prog), testosterone (Testo), medroxyprogesterone (MDRXY-Prog), levonorgestrel (Levo), norethindrone (Nore), estrone (E1), estradiol (E2), estriol (E3), and 17α-ethinylestradiol (EE2)) were investigated in sewage, WWTP effluents, receiving river water and sediments, and in drinking water plant (DWP) intakes. Steroids were detected in both dissolved and particulate phases with mean concentrations from 21 ng L−1 to 389 ng L−1 in raw sewage and from 10 ng L−1 to 296 ng L−1 in treated wastewater. The particle-associated steroids represented 0–82% of their total concentration as some steroids like E1 and E3 were detected only in the dissolved phase while MDRXY-Prog (81%), Nore (71%), and EE2 (>75%) were primarily detected in the particulate phase. Particle-associated steroids were detected in spring samples from river water with mean concentrations ranging from 5.4 ng L−1 to 35.7 ng L−1 compare to 3 ng L−1 to 6.8 ng L−1 in summer samples. Levels of particle-associated Testo, Nore, E2 and Levo in DWP intakes (406.2–13,149.1 ng g−1) were similar to those found in raw sewage (336.6–7628.8 ng g−1), indicating their persistence in the suspended phase from discharge points. Total steroids measured in sediments were in the range of 7–1213 ng g−1, 5–25 ng g−1, and 22–226 ng g−1 in autumn, spring, and summer, respectively. Our findings confirm the presence and seasonal variation of a mixture of particle-associated steroids in drinking water sources. The presence of high concentrations of a mixture of particle-associated steroids in DWP intakes highlight the need for highly effective particle-removal processes to eliminate these recalcitrant compounds during drinking water production. Finally, the detected concentrations raise concerns about their potential environmental effects.

Availability note (English)

Available from http://dx.doi.org/10.1016/j.scitotenv.2018.03.370

Additional details

Identifiers

DOI
10.1016/j.scitotenv.2018.03.370;
PII
S0048969718311306;

Publishing Information

Journal Title
Science of the Total Environment
Journal Volume
635
Journal Page Range
p. 144-155
ISSN
0048-9697
CODEN
STENDL

Optional Information

Copyright
Copyright (c) 2018 Elsevier B.V. All rights reserved.