|Titre :||A comparison of trends in wastewater-based data and traditional epidemiological indicators of stimulant consumption in three locations (2020)|
|Auteurs :||N. GOULDING ; M. HICKMAN ; M. REID ; E. J. AMUNDSEN ; J. A. BAZ-LOMBA ; J. W. O'BRIEN ; B. J. TSCHARKE ; P. DE VOOGT ; E. EMKE ; W. KUIJPERS ; W. HALL ; H. E. JONES|
|Type de document :||Article : Périodique|
|Dans :||Addiction (Vol.115, n°3, March 2020)|
|Article en page(s) :||462-472|
|Discipline :||EPI (Epidémiologie / Epidemiology)|
Thésaurus TOXIBASEEAUX USEES ; ANALYSE CHIMIQUE ; EPIDEMIOLOGIE DESCRIPTIVE ; COMPARAISON ; STIMULANTS ; EVOLUTION ; MDMA-ECSTASY ; METHAMPHETAMINE ; PURETE ; COCAINE ; METABOLITE ; MODELE STATISTIQUE
Thésaurus GéographiqueNORVEGE ; AUSTRALIE ; PAYS-BAS
AIMS: To compare long-term trends in wastewater data with other indicators of stimulant use in three locations and to test the reliability of estimates based on 1 week of sampling.
DESIGN: Comparison of trends in quantities ('loads') of stimulants or their metabolites in wastewater with trends in other indicators of stimulant use (e.g. treatment, police, population survey data).
SETTING AND PARTICIPANTS: Populations in Oslo (Norway), South-East Queensland (Australia) and Eindhoven (the Netherlands).
MEASUREMENTS: Wastewater data were modelled for MDMA (3,4-methylenedioxymethamphetamine), benzoylecgonine (a metabolite of cocaine), amphetamine and methamphetamine in Oslo; benzoylecgonine in Eindhoven; and methamphetamine in South-East Queensland. Choice of stimulants modelled in each region was primarily determined by availability of useable data.
FINDINGS: In Oslo, wastewater data, driving under the influence of drugs statistics and seizure data all suggested increasing MDMA use between 2009 and 2017. In South-East Queensland, there was an estimated 31.1% [95% confidence interval (CI) = 29.4-32.9%] annual increase in daily loads of methamphetamine in wastewater between 2009 and 2016, compared with a 14.1% (95% CI = 10.9-17.3%) annual increase in seizures. Some of the increase in wastewater can be explained by increased purity. In Eindhoven, there was no evidence of a change in cocaine consumption from wastewater, but a reduction was observed in numbers in treatment for cocaine use from 2012 to 2017. In approximately half the cases examined in Oslo, credible intervals around estimates of annual average loads from a regression model versus estimates based on a single week of sampling did not overlap.
CONCLUSIONS: Long-term trends in loads of stimulants in wastewater appear to be broadly consistent with trends in other indicators of stimulant use in three locations. Wastewater data should be interpreted alongside epidemiological indicators and purity data. One week of wastewater sampling may not be sufficient for valid inference about drug consumption.
|Domaine :||Drogues illicites / Illicit drugs|
|Refs biblio. :||47|
|Affiliation :||Population Health Sciences, University of Bristol, Canynge Hall, Bristol, UK|