Mitchell L.
Kim-Fu
a,
Ansel R.
Moll
b,
Esteban E.
Hernandez
a,
Boris
Droz
c,
Thierry N. J.
Fouquet
d and
Jennifer
Field
*e
aDepartment of Chemistry, Oregon State University, Corvallis, OR 97331, USA
bSchool of Chemical, Biological, and Environmental Engineering, Oregon State University, Corvallis, OR 97331, USA
cDepartment of Biological and Ecological Engineering, Oregon State University, Corvallis, OR 97331, USA
dBausch + Lomb Americas, Rochester, NY 14609, USA
eDepartment of Environmental and Molecular Toxicology, Oregon State University, Corvallis, OR 97331, USA. E-mail: jennifer.field@oregonstate.edu; Fax: +1-541-737-0497; Tel: +1-541-737-2265
First published on 9th December 2024
Correction for ‘Fluorinated aromatic PCBTF and 6:2 diPAP in bridge and traffic paints’ by Mitchell L. Kim-Fu et al., Environ. Sci.: Processes Impacts, 2024, https://doi.org/10.1039/D4EM00546E.
The corrected title and ‘Chemicals and solvents’ section are shown below:
Title: Fluorinated aromatic PCBTF and 6:2 diPAP in bridge and traffic paints
Chemicals and solvents
Solvents, PFAS standards of 11 target volatile PFAS [FTOHs, secondary FTOHs, perfluoroalkane sulfonamides (FASAs), and perfluoroalkane sulfonamido ethanols (FOSEs)], 55 target ionic PFAS [PFCAs, PFSAs, FASAs, perfluoroalkane sulfonamido acetic acids (FASAAs), substituted FASAs and FASAAs, fluorotelomer sulfonates, fluorotelomer carboxylic acids, diPAPs, chlorinated perfluoroalkyl ether sulfonates, perfluoroalkyl ether carboxylic acids, and cationic/zwitterionic PFAS], PCBTF (ThermoScientific, Waltham, MA), isotopically labeled extracted (surrogate) internal standards (Wellington, Guelph, ON), nonextracted internal standards, and reference fluoropolymers [PTFE, PCTFE, and Viton A] are listed in the ESI.†
The Royal Society of Chemistry apologises for these errors and any consequent inconvenience to authors and readers.
This journal is © The Royal Society of Chemistry 2025 |