“…A variety of aerobes can degrade PCBs, − but Paraburkholderia xenovorans strain LB400 demonstrates higher degradation efficacy for wide ranges of PCBs (mono- to hexa-chlorinated biphenyls). ,− PCB oxidation proceeds via the bph pathway; thus, bphA is commonly used as a biomarker because it encodes biphenyl dioxygenase, the initial catabolic enzyme in the pathway. ,, Specific carbon/energy sources (e.g., biphenyl, benzoate) are required for bph pathway induction, and many PCB congeners with 6 chlorines or less are cometabolized in the presence of biphenyl or benzoate. ,− Bioaugmenting sediments with suspended LB400 cells can efficiently oxidize LC-PCB congeners (up to trichlorinated homologues) and mitigate flux to the air. , Nevertheless, free cells often demonstrate unsatisfactory survivability and activity due to environmental fluctuations and nutrient availability − factors that can be moderated when cells exist as biofilms. Biofilms display increased gene expression levels and produce exopolysaccharides that improve stress tolerance and cell removal resistance. ,− Multiple studies have examined immobilized anaerobes that dechlorinate PCBs, ,− but comparatively few have focused on removing LC-PCBs through bioaugmentation of immobilized PCB-degrading aerobes to mitigate the direct human exposure pathway. − Improved LC-PCB bioremediation strategies require an enhanced understanding of immobilized PCB-degrading cells and how cells interact with surface materials.…”