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dc.contributor.authorPoma, Giulia
dc.contributor.authorSales Martínez, Carlos
dc.contributor.authorBruyland, Bram
dc.contributor.authorChristia, Christina
dc.contributor.authorGoscinny, Séverine
dc.contributor.authorVan Loco, Joris
dc.contributor.authorCovaci, Adrian
dc.date.accessioned2018-06-14T07:26:15Z
dc.date.available2018-06-14T07:26:15Z
dc.date.issued2018
dc.identifier.citationPOMA, Giulia; SALES MARTÍNEZ, Carlos; BRUYLAND, Bram; CHRISTIA, Christina; GOSCINNY, Séverine; VAN LOCO, Joris; COVACI, Adrian. (2018). Occurrence of Organophosphorus Flame Retardants and Plasticizers (PFRs) in Belgian Foodstuffs and Estimation of the Dietary Exposure of the Adult Population. Environmental Science & Technology, v. 4, n. 52, p. 2331-2338ca_CA
dc.identifier.urihttp://hdl.handle.net/10234/175143
dc.description.abstractThe occurrence of 14 organophosphorus fl ame retardants and plasticizers (PFRs) was investigated in 165 composite food samples purchased from the Belgian market and divided into 14 food categories, including fi sh, crustaceans, mussels, meat, milk, cheese, dessert, food for infants, fats and oils, grains, eggs, potatoes and derived products, other food (stocks), and vegetables. Seven PFRs [namely, tri- n -butyl phosphate (TnBP), tris(2-chloroethyl) phosphate (TCEP), tris(1- chloro-2-propyl) phosphate (TCIPP), tris(1,3-dichloro-2-propyl) phosphate (TDCIPP), triphenyl phosphate (TPHP), 2- ethylhexyldiphenyl phosphate (EHDPHP), and tris(2-ethylhexyl) phosphate (TEHP)] were detected at concentrations above quanti fi cation limits. Fats and oils were the most contaminated category, with a total PFR concentration of 84.4 ng/g of wet weight (ww), followed by grains (36.9 ng/g of ww) and cheese (20.1 ng/g of ww). Our results support the hypothesis that PFR contamination may occur during industrial processing and manipulation of food products (e.g., packaging, canning, drying, etc.). Considering the daily average intake of food for the modal adult Belgian (15 − 64 years of age), the dietary exposure to sum PFRs was estimated to be ≤ 7500 ± 1550 ng/day [103 ± 21 ng/kg of body weight (bw)/day]. For individual PFRs, TPHP contributed on average 3400 ng/day (46.6 ng/kg of bw/day), TCIPP 1350 ng/day (18.5 ng/kg of bw/day), and EHDPHP 1090 ng/day (15 ng/kg of bw/day), values that were lower than their corresponding health-based reference doses. The mean dietary exposure mainly originated from grains (39%), followed by fats and oils (21%) and dairy products (20%). No signi fi cant di ff erences between the intakes of adult men and women were observed.ca_CA
dc.format.extent8 p.ca_CA
dc.language.isoengca_CA
dc.publisherACS Publicationsca_CA
dc.relation.isPartOfEnvironmental Science & Technology (2018), v. 4, n. 52ca_CA
dc.rights.urihttp://rightsstatements.org/vocab/CNE/1.0/*
dc.subjectOrganophosphorus flame retardantca_CA
dc.subjectPlasticizers (PFRs)ca_CA
dc.subjectBelgian marketca_CA
dc.subjectFoodca_CA
dc.subjectPFR contaminationca_CA
dc.subjectIndustrial processingca_CA
dc.subjectManipulationca_CA
dc.titleOccurrence of Organophosphorus Flame Retardants and Plasticizers (PFRs) in Belgian Foodstuffs and Estimation of the Dietary Exposure of the Adult Populationca_CA
dc.typeinfo:eu-repo/semantics/articleca_CA
dc.identifier.doihttp://dx.doi.org/10.1021/acs.est.7b06395
dc.relation.projectIDFederal Public Service (FPS) Health, Food Chain Safety 479 and Environment, Project RT 14/12 FLAREFOOD, and the University of Antwerpca_CA
dc.rights.accessRightsinfo:eu-repo/semantics/restrictedAccessca_CA
dc.relation.publisherVersionhttps://pubs.acs.org/doi/10.1021/acs.est.7b06395ca_CA
dc.type.versioninfo:eu-repo/semantics/publishedVersionca_CA


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