Occurrence, variability and human exposure to Polychlorinated Dibenzo-p-dioxins (PCDDs), Polychlorinated Dibenzofurans (PCDFs) and Dioxin-Like Polychlorinated Biphenyls (DL-PCBs) in dairy products from Chile during the 2011–2013 survey. (May 2015)

• Record Type: Journal Article
• Authors: Pizarro-Aránguiz, N.; Galbán-Malagón, C.J.; Ruiz-Rudolph, P.; Araya-Jordan, C.; Maddaleno, A.; San Martin, B.
• Is Part Of: Chemosphere. Volume 126(2015)
• Page Start: 78
• Page End: 87
• Publication Date: 2015-05
• Subjects: Dioxins -- PCDD/Fs -- DL-PCBs -- POPs -- Milk -- Butter and human exposure assessment; Pollution -- Periodicals; Pollution -- Physiological effect -- Periodicals; Environmental sciences -- Periodicals; Atmospheric chemistry -- Periodicals; 551.511
• DOI: 10.1016/j.chemosphere.2014.10.087
• Languages: English
• ISSNs: 0045-6535

Abstract

Highlights: We analyzed PCDD/Fs and DL-PCBs concentration in milk and Butter samples from Chilean Producers. Human exposure to PCDD/Fs and DL-PCBs was assessed for Adult and Children. Concentrations obtained were in the lower range of the reported in the literature. Higher concentrations for PCDD/Fs and DL-PCBs were found in highly populated and industrialized regions. Abstract: Levels, congener profiles of PCDD/Fs, DL-PCBs and human exposure for these xenobiotics never have been reported in Chile. For that purpose 102 raw cow milk samples were collected from seven different regions of Chile during 2011 until 2013. The highest mean level for PCDD/Fs, corresponds to 0.32 pg WHO-TEQ2005 g −1 fat (2012) and for DL-PCBs 0.17 pg WHO-TEQ2005 g −1 fat (2011), using the upper bound approach. Penta and tetra chlorinated congeners dominated PCDD/Fs profiles in a WHO-TEQ2005 basis during the survey. In the case of DL-PCBs, PCB 126 dominated the profiles with 89%. Statistical analysis showed significant difference among years only in DL-PCBs residues. Also dietary intake was estimated, and the highest level for total sum of PCDD/Fs and DL-PCBs for adult was 0.16 pg WHO-TEQ kg −1 b.w d −1 (2011) and for children correspond to 0.65 pg WHO-TEQ kg −1 b.w d −1 (2011). Concentrations and dietary intake for the studied compounds in milk and butter samples were below international and national regulations.