Toxicokinetic study of dioxins and furans in laying chickens.
Since foodstuffs from animal origin and particularly poultry products have been pointed out several times as reservoir of dioxins and related compounds, notably in Belgium few years ago, food chain safety issues appeared. Although food chain contamination incidents occurred many times through contaminated feedstuffs consumption in commercial chicken farms, very few studies have been carried out on transfer of dioxins and related compounds from commercial feed to hens. The present work continues a preliminary study on dioxin transfer in laying chickens carried out in our lab and available on-line on November 2004 in Environment International. In this work, absorption of dioxins were not preferential for 2,3,7,8-substituted congeners, increase with increasing number of chlorines, and was not linearly dependent of the octanol/water partition. Only 2,3,7,8-congeners were found in all organs studied, and these latter showed the same congener profile and similar lipid-normalized concentration, except for the liver. Abdominal fat and liver seemed to be the major storage sites and the liver preferentially retained highly chlorinated congeners. Unfortunately in this previous trial, laying process stopped very early for unknown reason leading to a considerable lost of information. In the present toxicokinetic study, more complete gastrointestinal absorption, excretion in eggs and bioaccumulation of dioxins in different tissues were investigated in chickens fed for 14 weeks with a 9 ng TEQ/kg contaminated feed. Stable levels were reached after 7 weeks in excreta and 9 weeks in eggs. During the whole trial, gastrointestinal absorption ranged between 41% and 91% depending on the congener. At steady state conditions, excretion of 1,2,3,4,6,7,8-HpCDD, OCDD, 1,2,3,4,6,7,8-HpCDF and OCDF exceeded 100% demonstrating excretion from tissues of these congeners which were also the most abundant in feed. 1,2,3,7,8-PeCDD, 1,2,3,7,8-PeCDF, 2,3,4,7,8-PeCDF, 1,2,3,6,7,8-HxCDF, 1,2,3,7,8,9-HxCDF and 2,3,4,6,7,8-HxCDF seemed to be metabolized more efficiently. Lipid adjusted concentrations and pattern were unexpectedly similar in the abdominal fat and the liver. On the contrary, eggs and breast muscles showed different pattern with higher level for high chlorinated congeners. When extrapolating our results, we found that a feed containing 0.750 ng TEQ/kg of dioxins (European norm for feedstuff) would cause a level lower than the maximum threshold level of 3 pg TEQ/g fat for chicken eggs fixed by European Communities. Nevertheless, a concentration lower than 0.6 ng TEQ/kg in feed would be needed to produce breast muscles less contaminated than 2 pg TEQ/g fat authorized in European.
Pirard
Catherine
C
Mass Spectrometry Laboratory, University of Liège, Allée de la Chimie 3, Bat. B6c Sart-Tilman B-4000 Liège, Belgium. Catherine.Pirard@ulg.ac.be
De Pauw
Edwin
E
D000042:Absorption; D000273:Adipose Tissue / Q000378:metabolism; D000821:Animal Feed; D000818:Animals; D001530:Belgium; D001572:Benzofurans / Q000493:pharmacokinetics / Q000633:toxicity; D001940:Breast / Q000378:metabolism; D002645:Chickens; D000072338:Dibenzofurans, Polychlorinated; D004147:Dioxins / Q000493:pharmacokinetics* / Q000633:toxicity; D004531:Eggs; D005506:Food Contamination / Q000032:analysis*; D005663:Furans / Q000493:pharmacokinetics* / Q000633:toxicity; D008099:Liver / Q000378:metabolism; D000072317:Polychlorinated Dibenzodioxins / Q000493:pharmacokinetics / Q000633:toxicity; D012989:Soil Pollutants / Q000493:pharmacokinetics* / Q000633:toxicity; D013997:Time Factors; D014018:Tissue Distribution
D001572:Benzofurans; D000072338:Dibenzofurans, Polychlorinated; D004147:Dioxins; D005663:Furans; D000072317:Polychlorinated Dibenzodioxins; D012989:Soil Pollutants