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3859267 
Journal Article 
Production of perfluorinated carboxylic acids (PFCAs) from the biotransformation of polyfluoroalkyl phosphate surfactants (PAPS): exploring routes of human contamination 
D'Eon, JC; Mabury, SA 
2007 
Environmental Science & Technology
ISSN: 0013-936X
EISSN: 1520-5851 
41 
13 
4799-4805 
English 
Perfluorinated acids are detected in human blood world-wide, with increased levels observed in industrialized areas. The origin of this contamination is not well understood. A possible route of exposure, which has received little attention experimentally, is indirect exposure to perfluorinated acids through ingestion of chemicals applied to food contact paper packaging. The current investigation quantified the load of perfluorinated acids to Sprague-Dawley rats upon exposure to polyfluoroalkyl phosphate surfactants (PAPS), nonpolymeric fluorinated surfactants approved for application to food contact paper products. The animals were administered a single dose at 200 mg/kg by oral gavage of 8:2 fluorotelomer alcohol (8:2 FTOH) mono-phosphate (8:2 monoPAPS), or the corresponding di-phosphate (8:2 diPAPS), with blood taken over 15 days post-dosing to monitor uptake, biotransformation, and elimination. Upon completion of the time-course study the animals were redosed using an identical dosing procedure, with sacrifice and necropsy 24 h after the second dosing. Increased levels of perfluorooctanoic acid (PFOA), along with both 8:2 PAPS congeners, were observed in the blood of the dosed animals. In the 8:2 monoPAPS-dosed animals, 8:2 monoPAPS and PFOA blood concentrations peaked at 7900 +/- 1200 ng/g and 34 +/- 4 ng/g respectively. In the 8:2 diPAPS-dosed animals, 8:2 diPAPS peaked in concentration at 32 +/- 6 ng/g, and 8:2 monoPAPS and PFOA peaked at 900 +/- 200 ng/g and 3.8 +/- 0.3 ng/g, respectively. Several established polyfluorinated metabolites previously identified in 8:2 FTOH metabolism studies were also observed in the dosed animals. Consistent with other fluorinated contaminants, the tissue distributions showed increased levels of both PFOA and the 8:2 PAPS congeners in the liver relative to the other tissues measured. Previous investigations have found that PAPS can migrate into food from paper packaging. Here we link ingestion of PAPS with in vivo production of perfluorinated acids. 
PFAS
• 6:2/8:2 diPAP
     Literature Search
          Pubmed
     Screening Results
          Excluded/Not on Topic
• 6:2 diPAP
     Literature Search
          Pubmed
     Screening Results
          Excluded/Not on Topic
• 8:2 diPAP
     Literature Search
          Pubmed
     Screening Results
          Toxicokinetic studies
               ADME
• Additional PFAS (formerly XAgency)
• Expanded PFAS SEM (formerly PFAS 430)
     Litsearch: September 2019
          PubMed
     Screened Studies
          Supplemental
     3:2 Fluorotelomer alcohol
• FtOH 8:2
     Literature Search
          Pubmed
     Screening Results
          Excluded/Not on Topic
• ^Per- and Polyfluoroalkyl Substances (PFAS)
     FtOH 8:2 (678-39-7)
          Literature Search
               Pubmed
     6:2 diPAP (57677-95-9)
          Literature Search
               Pubmed
     8:2 diPAP (678-41-1)
          Literature Search
               Pubmed
     6:2/8:2 diPAP (943913-15-3)
          Literature Search
               Pubmed
• PFAS 150
     Literature Search August 2019
          PubMed
     Not prioritized for screening
     8:2 Fluorotelomer alcohol
     Ammonium perfluorooctanoate
     Perfluorooctanoic acid
• Yale PFAS Liver study