2017
DOI: 10.1016/j.fct.2016.12.011
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Dietary intake of phosphorus flame retardants (PFRs) using Swedish food market basket estimations

Abstract: The occurrence of eight phosphorus flame retardants (PFRs) was investigated in 53 composite food samples from 12 food categories, collected in 2015 for a Swedish food market basket study. 2-ethylhexyl diphenyl phosphate (EHDPHP), detected in most food categories, had the highest median concentrations (9 ng/g ww, pastries). It was followed by triphenyl phosphate (TPHP) (2.6 ng/g ww, fats/oils), tris(1,3-dichloro-2-propyl) phosphate (TDCIPP) (1.0 ng/g ww, fats/oils), tris(2-chloroethyl) phosphate (TCEP) (1.0 ng/… Show more

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Cited by 161 publications
(119 citation statements)
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References 43 publications
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“…Our measured median concentrations of PFRs (Figure 3) were comparable with the levels detected in edible insects and insect-based food for human consumption from our previous study (Poma et al 2017a). In the same way, the median contamination with PFRs and plasticizers in insect samples was similar between the EU, PRC, and JPN/SK, always dominated by aromatic-PFRs (see Figure S2) and DEHP, and was comparable with median levels measured in foodstuffs of animal origin from worldwide studies (Cariou et al 2016;Cheng et al 2016;Ding et al 2018;He et al 2015;Poma et al 2017bPoma et al , 2018Van Holderbeke et al 2014;Wang and Kannan 2018;Yang et al 2018). For these two groups of compounds, the contamination in the insects could have occurred during production [e.g., from the rearing substrate, from the polyvinyl chloride (PVC) gloves used by workers during insect rearing and handling, etc.…”
Section: Discussionsupporting
confidence: 75%
See 1 more Smart Citation
“…Our measured median concentrations of PFRs (Figure 3) were comparable with the levels detected in edible insects and insect-based food for human consumption from our previous study (Poma et al 2017a). In the same way, the median contamination with PFRs and plasticizers in insect samples was similar between the EU, PRC, and JPN/SK, always dominated by aromatic-PFRs (see Figure S2) and DEHP, and was comparable with median levels measured in foodstuffs of animal origin from worldwide studies (Cariou et al 2016;Cheng et al 2016;Ding et al 2018;He et al 2015;Poma et al 2017bPoma et al , 2018Van Holderbeke et al 2014;Wang and Kannan 2018;Yang et al 2018). For these two groups of compounds, the contamination in the insects could have occurred during production [e.g., from the rearing substrate, from the polyvinyl chloride (PVC) gloves used by workers during insect rearing and handling, etc.…”
Section: Discussionsupporting
confidence: 75%
“…The EDI-estimation resulted similar for Europe and Asia and comparable with levels generally estimated for the same groups of compounds in common food of animal origin worldwide (Ding et al 2018;Giovanoulis et al 2018;Poma et al 2017bPoma et al , 2018Qian et al 2017;Wang et al , 2019Yang et al 2018). However, when making this comparison, it is important to consider that the estimated dietary intake can vary strongly among countries, likely due to differences in dietary habits of the population, number, and typology of food items included in the food categories as well as individual targeted compounds considered within a group of chemicals, etc.…”
Section: Evaluation Of Chemical Safety Of Edible Insectssupporting
confidence: 78%
“…Few studies have estimated the relative contribution from dust to the total exposure of OPEs. Poma et al estimated that the intake of OPEs from dust in Swedish adults were in the same order of magnitude as the intake via the diet [162]. However, the relative contribution for different OPEs varied.…”
Section: Relative Contribution From Dust To the Total Intakementioning
confidence: 99%
“…For volatile or semi-volatile PEFRs (e.g., TCEP, tris(1-chloro-2propyl) phosphate -TCIPP), air and suspended particles inhalation may be a significant intake pathway (Schreder et al, 2016;Xu et al, 2016;He et al, 2018c). Ingestion of contaminated food (e.g., by migration from plastic packaging) may contribute to oral intake of PEFRs, but its contribution appears to vary substantially between compounds, as well as between and within populations (Zhang et al, 2016;Zheng et al, 2016;Xu et al, 2017;Poma et al, 2017Poma et al, , 2018.…”
Section: Environmental Occurrence and Routes Of Exposurementioning
confidence: 99%