Elsevier, Chemosphere, (168), p. 1032-1041
DOI: 10.1016/j.chemosphere.2016.10.107
Full text: Download
The popularity of new psychoactive substances (NPS) has grown in recent years, with certain NPS commonly and preferentially consumed even following the introduction of preventative legislation. With the objective to improve the knowledge on the use of NPS, a rapid and very sensitive method was developed for the determination of ten priority NPS (N-ethylcathinone, methylenedioxypyrovalerone (MDPV), methylone, butylone, methedrone, mephedrone, naphyrone, 25-C-NBOMe, 25-I-NBOMe and 25-B-NBOMe) in influent wastewater. Sample clean-up and pre-concentration was made by off-line solid phase extraction (SPE) with Oasis MCX cartridges. Isotopically labelled internal standards were used to correct for matrix effects and potential SPE losses. Following chromatographic separation on a C18 column within 6 min, the compounds were measured by tandem mass spectrometry in positive ionization mode. The method was optimised and validated for all compounds. Limits of quantification were evaluated by spiking influent wastewater samples at 1 or 5 ng/L. An investigation into the stability of these compounds in influent wastewater was also performed, showing that, following acidification at pH 2, all compounds were relatively stable for up to 7 days. The method was then applied to influent wastewater samples from eight European countries, in which mephedrone, methylone and MDPV were detected. This work reveals that although NPS use is not as extensive as for classic illicit drugs, the application of a highly sensitive analytical procedure makes their detection in wastewater possible. The developed analytical methodology forms the basis of a subsequent model-based back-calculation of abuse rate in urban areas (i.e. wastewater-based epidemiology). ; The authors would like to thank all the personnel of the wastewater treatment plants for their collaboration in providing the samples: Sociedad de Fomento Agrícola Castellonense (FACSA, Castellon, Spain), VEAS (Oslo, Norway), Aquiris (Brussels, Belgium), Hoogheemraadschap de Stichtse Rijnlanden (Utrecht, the Netherlands), Wessex Water (Bristol, UK), Metropolitana Milanese (Milan, Italy), Werdhölzli (Zurich, Switzerland) and BIOFOS (Copenhagen, Denmark). RB, JBL, EC, AC, JK, AKM, PR and NIR acknowledge the European Union for their Early Stage Researcher (ESR) contracts and EGL for her Experienced Researcher (ER) contract as part of the EU-International Training Network SEWPROF (Marie Curie- PEOPLE Grant #317205). LB acknowledges NPS-Euronet (HOME/2014/JDRUG/AG/DRUG/7086), co-funded by the European Union, for his post-doctoral fellowship. This publication reflects the views only of the authors, and the European Commission cannot be held responsible for any use which may be made of the information contained therein. AvN acknowledges the support of the Flanders Foundation for Research (FWO). EGL is also thankful for the financial support from Generalitat Valenciana (APOSTD/2015, Programa VALi+d). The financial support of Generalitat Valenciana and of the Spanish Ministry of Economy and Competitiveness (Project ref CTQ2015-65603) is also acknowledged by the authors of University Jaume I.