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. 2022 Feb 28;56(6):3699–3709. doi: 10.1021/acs.est.1c07608

Table 2. Treatment of a Concentrated PFAS Mixture in NaCl Brine by UV/S + Ia.

PFAS category compound PFAS concentration (μg L–1) total fluorine in C–F bonds (μg L–1) residual PFAS after 24 h (μg L–1)b parent PFAS removal ratio (%)
FTSAs 4:2 FTS 131 68 63 51.9
  6:2 FTS 27,950 16,124 296 98.9
  8:2 FTS 875 535 <53 >93.9
PFCAs PFBA 1950 1212 <5 >99.7
  PFPeA 5872 3803 <13 >99.7
  PFHxA 16,433 10,936 <8 >99.9
  PFHpA 7492 5083 <9 >99.8
  PFOA 101,550 69,896 <10 >99.9
  PFNA 228 159 <12 >94.7
PFSAs PFBS 4988 2522 279 94.4
  PFHxS 72,550 40,893 <88 >99.8
  PFOS 86,950 56,155 <100 >99.8
sum   327.0 mg L–1 207.4 mg L–1 (10.9 mM) <0.9 mg L–1 >99.7
a

Reaction conditions: the 3% NaCl brine with the tabulated components was diluted with 1:1 DI water, Na2SO3 (10 mM), KI (2 mM), NaHCO3 (5 mM), pH 12.0, 254 nm irradiation (an 18 W low-pressure Hg lamp in 600 mL solution), and 20 °C.

b

Concentrations without a definitive value indicate the limit of quantitation by the HRMS instrument in our study. These values are the HRMS-detected concentration multiplied by 2 (due to the 1:1 dilution before treatment). Solid-phase extraction for accurate quantitation in low concentration ranges (e.g., the prevalent 70 ng L–1 reference for drinking water) was not used in this proof-of-concept study.