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2 ids (including alkanes, alcohols, toluene, n-perfluorooctane, CCl(4), and DMSO) as a function of the
7 tion to soils, while transformation products perfluorooctane sulfonamide (FOSA) and PFOS are sufficie
8 ied for PFOAAmS and three products including perfluorooctane sulfonamide (FOSA) for PFOSAmS through h
9 of 13 perfluorinated alkyl acids (PFAAs) and perfluorooctane sulfonamide (FOSA) in primiparous women
10 collected, perfluorooctane sulfonate (PFOS), perfluorooctane sulfonamide (FOSA), and C8-C14 perfluoro
11 tro metabolite from the pre-2002 product was perfluorooctane sulfonamide (FOSA), and coincident with
14 sis by examining the isomer-specific fate of perfluorooctane sulfonamide (PFOSA), a known PFOS-precur
15 ecanoate (PFDeA), perfluorononanoate (PFNA), perfluorooctane sulfonamide (PFOSA), perfluorooctane sul
16 In the current work, concentrations of PFOS, perfluorooctane sulfonamide (PFOSA), PFOS isomer profile
17 and 21% for PCB congeners 118, 167, 209, and perfluorooctane sulfonamide in females; and between 17%
19 perfluorooctane sulfonate and its precursor perfluorooctane sulfonamide varied among tissues from 9
20 l (PCBs 138, 153, 167, 170, 195, and 209 and perfluorooctane sulfonamide) and paternal (PCBs 172 and
21 cetate, N-ethyl perfluorooctane sulfonamide, perfluorooctane sulfonamide, and perfluorooctane sulfona
23 perfluorooctane sulfonamidoacetate, N-ethyl perfluorooctane sulfonamide, perfluorooctane sulfonamide
24 about the stability of high-molecular-weight perfluorooctane sulfonamide-based substances such as the
25 forming an important intermediate precursor (perfluorooctane sulfonamide: FOSA), into a prevalent com
26 s (FTMACs), fluorotelomer acrylates (FTACs), perfluorooctane sulfonamides (FOSAs), and perfluorooctan
27 s (FTMACs), fluorotelomer acrylates (FTACs), perfluorooctane sulfonamides (FOSAs), and perfluorooctan
28 nd numerous PFAA-precursors (i.e., (N-alkyl) perfluorooctane sulfonamides and fluorotelomer carboxyli
30 observed between SAmPAP diester and N-ethyl perfluorooctane sulfonamido acetate (an anticipated degr
31 w molecular weight substances (e.g., N-ethyl perfluorooctane sulfonamido ethanol (EtFOSE)) in wastewa
32 uorohexanesulfonate (PFHxS), and 2-(N-methyl-perfluorooctane sulfonamido) acetate (Me-PFOSA-AcOH) wer
34 N-ethyl perfluorooctane sulfonamidoacetate, perfluorooctane sulfonamidoacetate, N-ethyl perfluorooct
35 ed to a suite of products, including N-ethyl perfluorooctane sulfonamidoacetate, perfluorooctane sulf
36 he observed metabolites in fish were N-ethyl perfluorooctane sulfonamidoacetic acid, perfluorooctane
37 thyl perfluorooctane sulfonamidoacetic acid, perfluorooctane sulfonamidoacetic acid, perfluorooctane
42 were detected regularly in peat samples with perfluorooctane sulfonate (85-655 ng kg(-1)), perfluoroo
43 ch concentrations either remained unchanged (perfluorooctane sulfonate (PFOS) and perfluorocarboxylat
53 and 0.91 ng g(-1) ww, respectively, whereas perfluorooctane sulfonate (PFOS) concentrations did not
55 st concentrations in the earthworms were for perfluorooctane sulfonate (PFOS) in the AFFF-impacted So
61 h suggests perfluorooctanoic acid (PFOA) and perfluorooctane sulfonate (PFOS) may be associated with
63 -ng/mL increase in simulated cord plasma for perfluorooctane sulfonate (PFOS) was 2.72 g (95% CI: -3.
66 n of serum perfluorooctanoic acid (PFOA) and perfluorooctane sulfonate (PFOS) with self-reported preg
67 ulfonate (PFHxS), perfluorooctanoate (PFOA), perfluorooctane sulfonate (PFOS), and perfluorononanoic
68 PFAAs), including perfluorooctanoate (PFOA), perfluorooctane sulfonate (PFOS), and perfluorononanoic
69 (PFNA), perfluorooctane sulfonamide (PFOSA), perfluorooctane sulfonate (PFOS), and perfluorooctanoic
70 nyls (OH-PCBs), pentachlorophenol (PCP), and perfluorooctane sulfonate (PFOS), compete with thyroxin
71 ) prenatal plasma perfluorooctanoate (PFOA), perfluorooctane sulfonate (PFOS), perfluorohexane sulfon
72 rations of PFASs [perfluorooctanoate (PFOA), perfluorooctane sulfonate (PFOS), perfluorononanoate (PF
73 entrations of perfluorooctanoic acid (PFOA), perfluorooctane sulfonate (PFOS), perfluorononanoic acid
75 s the 147 biota samples (18 taxa) collected, perfluorooctane sulfonate (PFOS), perfluorooctane sulfon
76 Previously measured median concentrations of perfluorooctane sulfonate (PFOS), perfluorooctanoate (PF
77 ciations of prenatal serum concentrations of perfluorooctane sulfonate (PFOS), perfluorooctanoate (PF
78 gations into the biodegradation potential of perfluorooctane sulfonate (PFOS)-precursor candidates ha
83 1.7 (95% confidence interval: 1.0, 2.8) for perfluorooctane sulfonate and 2.1 (95% confidence interv
84 The concentration ratios (+/-SE) between perfluorooctane sulfonate and its precursor perfluorooct
85 sk in boys per quartile of maternal level of perfluorooctane sulfonate and perfluorooctanoic acid (P
88 id), PFBS (perfluorobutane sulfonate), PFOS (perfluorooctane sulfonate), and PFOA (perfluorooctanoic
89 (PFCs), including perfluorooctanoic acid and perfluorooctane sulfonate, are manmade chemicals that ha
90 born to mothers in the lowest quartiles: for perfluorooctane sulfonate, beta = -0.18 (95% confidence
91 cept for March-April, when concentrations of perfluorooctane sulfonate, perfluorooctanoate, and numer
92 f PFCs, including perfluorooctanoic acid and perfluorooctane sulfonate, were positively associated wi
96 ) concentrations in breast milk, we measured perfluorooctane sulfonic (PFOS) and perfluorooctanoic ac
97 s with the highest serum concentrations were perfluorooctane sulfonic acid (PFOS) and perfluorooctano
98 ng studies have shown that concentrations of perfluorooctane sulfonic acid (PFOS) in men are higher t
102 s), including perfluorooctanoic acid (PFOA), perfluorooctane sulfonic acid (PFOS), perfluorohexane su
103 Cs, including perfluorooctanoic acid (PFOA), perfluorooctane sulfonic acid (PFOS), perfluorononanoic
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