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Bioavailability of phthalate and DINCH® plasticizers, after oral administration of dust to piglets

Zugehörigkeit
Bavarian Health and Food Safety Authority, Department of Chemical Safety and Toxicology, Munich, Germany
Plichta, V.;
Zugehörigkeit
Bavarian Health and Food Safety Authority, Department of Chemical Safety and Toxicology, Munich, Germany
Völkel, W.;
Zugehörigkeit
Bavarian Health and Food Safety Authority, Department of Chemical Safety and Toxicology, Munich, Germany
Fembacher, L.;
Zugehörigkeit
German Federal Institute for Risk Assessment, Berlin, Germany
Spolders, M.;
Zugehörigkeit
Bavarian Health and Food Safety Authority, Department of Chemical Safety and Toxicology, Munich, Germany
Wöckner, M.;
Zugehörigkeit
Bavarian Health and Food Safety Authority, Department of Chemical Safety and Toxicology, Munich, Germany
Aschenbrenner, B.;
Zugehörigkeit
German Federal Institute for Risk Assessment, Berlin, Germany
Schafft, H.;
Zugehörigkeit
Bavarian Health and Food Safety Authority, Department of Chemical Safety and Toxicology, Munich, Germany
Fromme, H.

For decades, phthalates have been widely used as plasticizers in a large number of consumer products, leading to a complex exposure to humans via ingestion, inhalation or dermal uptake. Children may have a higher unintended dust intake per day compared to adults. Therefore, dust intake of children could pose a relevant exposure and subsequently a potential health risk. The aim of this study was to determine the relative bioavailability of certain phthalates, such as di(2-ethylhexyl) phthalate (DEHP), di-isononyl phthalate (DINP) and the non-phthalate plasticizer diisononyl 1,2-cyclohexanedicarboxylic acid (DINCH®, Hexamoll®), after ingestion of dust. Seven 5-week-old male piglets were fed five different dust samples collected from daycare centers. Overall, 0.43 g to 0.83 g of dust sieved to 63 μm were administered orally. The piglets’ urine was collected over a period of 38 h. The excreted metabolites were quantified using an LC–MS/MS method. The mean uptake rates of the applied doses for DEHP, DINP, and DINCH® were 43% ± 11%, 47% ± 26%, and 9% ± 3.5%, respectively. The metabolites of DEHP and DINP showed maximum concentrations in urine after three to five hours, whereas the metabolites of DINCH®, reached maximum concentrations 24 h post-dose. The oral bioavailability of the investigated plasticizers was higher compared to the bioaccessibility reported from in vitro digestion tests. Furthermore, the bioavailability of DEHP did not vary substantially between the dust samples, whereas a dose-dependent saturation process for DINP was observed. In addition to other intake pathways, dust could be a source of plasticizers in children using the recent intake rates for dust ingestion.

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