Per- and polyfluoroalkyl substances (PFASs) from aqueous
film forming
foams (AFFFs) can hinder bioremediation of co-contaminants such as
trichloroethene (TCE) and benzene, toluene, ethylbenzene, and xylene
(BTEX). Anaerobic dechlorination can require bioaugmentation of Dehalococcoides, and for BTEX, oxygen is often sparged to
stimulate in situ aerobic biodegradation. We tested PFAS inhibition
to TCE and BTEX bioremediation by exposing an anaerobic TCE-dechlorinating
coculture, an aerobic BTEX-degrading enrichment culture, and an anaerobic
toluene-degrading enrichment culture to n-dimethyl
perfluorohexane sulfonamido amine (AmPr-FHxSA), perfluorohexane sulfonamide
(FHxSA), perfluorohexanesulfonic acid (PFHxS), or nonfluorinated surfactant
sodium dodecyl sulfate (SDS). The anaerobic TCE-dechlorinating coculture
was resistant to individual PFAS exposures but was inhibited by >1000×
diluted AFFF. FHxSA and AmPr-FHxSA inhibited the aerobic BTEX-degrading
enrichment. The anaerobic toluene-degrading enrichment was not inhibited
by AFFF or individual PFASs. Increases in amino acids in the anaerobic
TCE-dechlorinating coculture compared to the control indicated stress
response, whereas the BTEX culture exhibited lower concentrations
of all amino acids upon exposure to most surfactants (both fluorinated
and nonfluorinated) compared to the control. These data suggest the
main mechanisms of microbial toxicity are related to interactions
with cell membrane synthesis as well as protein stress signaling.