2009
DOI: 10.1007/s10311-009-0253-7
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Occurrence of pharmaceuticals and hormones in drinking water treated from surface waters

Abstract: International audienceThe levels of a wide variety of pharmaceuticals and hormones, in source and potable-water supplies of French drinking water treatment plants, were assessed. In surface waters, 27 of the 51 target compounds were determined at least once. Paracetamol, salicylic acid and carbamazepine were quantified in more than 80% of samples. The highest concentration of 71 ng/L was observed for paracetamol. Twelve other substances were widely found in the surface waters studied, contaminating between 33 … Show more

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Cited by 214 publications
(103 citation statements)
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“…Multiple-classes of pharmaceuticals have been detected in DWSs in countries such as the United States (U.S.) (Benotti et al, 2009;Focazio et al, 2008), Canada (Kleywegt et al, 2011) and several European countries (de Jongh et al, 2012;Kuch Contents lists available at ScienceDirect journal homepage: www.elsevier.com/locate/ecoenv and Ballschmiter, 2001; Mompelat et al, 2011;Valcárcel et al, 2013;Vulliet et al, 2011). In a national survey performed by the U.S. Geological Survey, several classes of pharmaceuticals, including antibiotics, prescription drugs, non-prescription drugs and other wastewater-related drugs, were detectable (Focazio et al, 2008), and the maximum concentrations of the detected pharmaceuticals ranged from 0.019 μg/L to 0.30 μg/L.…”
Section: Introductionmentioning
confidence: 99%
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“…Multiple-classes of pharmaceuticals have been detected in DWSs in countries such as the United States (U.S.) (Benotti et al, 2009;Focazio et al, 2008), Canada (Kleywegt et al, 2011) and several European countries (de Jongh et al, 2012;Kuch Contents lists available at ScienceDirect journal homepage: www.elsevier.com/locate/ecoenv and Ballschmiter, 2001; Mompelat et al, 2011;Valcárcel et al, 2013;Vulliet et al, 2011). In a national survey performed by the U.S. Geological Survey, several classes of pharmaceuticals, including antibiotics, prescription drugs, non-prescription drugs and other wastewater-related drugs, were detectable (Focazio et al, 2008), and the maximum concentrations of the detected pharmaceuticals ranged from 0.019 μg/L to 0.30 μg/L.…”
Section: Introductionmentioning
confidence: 99%
“…In a national survey performed by the U.S. Geological Survey, several classes of pharmaceuticals, including antibiotics, prescription drugs, non-prescription drugs and other wastewater-related drugs, were detectable (Focazio et al, 2008), and the maximum concentrations of the detected pharmaceuticals ranged from 0.019 μg/L to 0.30 μg/L. Not all pharmaceuticals are completely removed during drinking-water treatment processes (Benotti et al, 2009;Huerta-Fontela et al, 2011;Stackelberg et al, 2007;Vulliet et al, 2011). As a result, several pharmaceuticals, such as carbamazepine, lincomycin, ibuprofen, acetaminophen, erythromycin, roxithromycin and metoprolol, are also detectable in distribution waters (Delgado et al, 2012;Stackelberg et al, 2004;Vulliet et al, 2011).…”
Section: Introductionmentioning
confidence: 99%
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“…Among all the sample matrices, flush water contained the most progestagens with the highest concentrations (total concentrations more than 10,000 ng/L), followed by feces (total concentrations nearly 6,000 ng/g). Previous studies reported that progesterone was detected in piled manure in USA at the concentration of 196 ng/g [20] and progesterone and norgestrel in flush [9], [11], [12], [20], [30], [31], [33], [34], [35], [36] AD anordrin, CMD chlormadinone, CMDA chlormadinone acetate, CPRA cyproterone acetate, DGT dydrogesterone, 5α-DHP samples from a swine farm in Guangxi (China) with their concentrations above 10,000 ng/L [32]. In the WWTP, influent contained the most progestagens (total concentrations up to 81 ng/L), followed by dewatered sludge (total concentrations up to 23 ng/g).…”
Section: Application To Environmental Samplesmentioning
confidence: 99%
“…A clear example is given by a combined O 3 /UV treatment of ketoprofen: the transformation products were much more toxic than 6 ketoprofen itself and this parameter could be reduced only by increasing the operational time, with consequent repercussion of the economic sustainability of the process (Illés et al 2014). Due to the limited effectiveness of WTPs towards a complex mixture of EDCs, micropollutants can re-enter the water cycle accumulating even into drinking waters (Benotti et al 2009, Lundstrom et al 2010, Mompelat et al 2009, Touraud et al 2011, Vulliet et al 2011). Sun and collaborators (2013) collected data worldwide, associating the major long-term ecological risk of municipal effluents and reclaimed waters to the presence of steroid estrogens and phenolic compounds.…”
Section: Introductionmentioning
confidence: 99%