Physical and Biological Release of Poly- and Perfluoroalkyl Substances (PFASs) from Municipal Solid Waste in Anaerobic Model Landfill Reactors

• Published in: Environmental science & technology Vol. 49; no. 13; pp. 7648 - 7656
• Main Authors: Allred, B. McKay, Lang, Johnsie R, Barlaz, Morton A, Field, Jennifer A
• Format: Journal Article
• Language: English
• Published: United States American Chemical Society 07.07.2015
• Subjects: acetic acid; anaerobic digesters; bioactive properties; Biodegradation; Biodegradation, Environmental; Bioreactors; Garbage; Hydrocarbons, Fluorinated - analysis; Hydrocarbons, Fluorinated - chemistry; Landfill; landfill leachates; landfills; Leachates; Leaching; Methane - metabolism; methane production; methanogens; Models, Theoretical; Municipal solid waste; Perfluoroalkyl & polyfluoroalkyl substances; perfluorocarbons; Refuse Disposal - instrumentation; Refuse Disposal - methods; Solid Waste; Surface water; Waste Disposal Facilities; Water Pollutants, Chemical - analysis
• ISSN: 0013-936X; 1520-5851; 1520-5851
• DOI: 10.1021/acs.est.5b01040

A wide variety of consumer products that are treated with poly- and perfluoroalkyl substances (PFASs) and related formulations are disposed of in landfills. Landfill leachate has significant concentrations of PFASs and acts as secondary point sources to surface water. This study models how PFASs enter leachate using four laboratory-scale anaerobic bioreactors filled with municipal solid waste (MSW) and operated over 273 days. Duplicate reactors were monitored under live and abiotic conditions to evaluate influences attributable to biological activity. The biologically active reactors simulated the methanogenic conditions that develop in all landfills, producing ∼140 mL CH4/dry g refuse. The average total PFAS leaching measured in live reactors (16.7 nmol/kg dry refuse) was greater than the average for abiotic reactors (2.83 nmol/kg dry refuse), indicating biological processes were primarily responsible for leaching. The low-level leaching in the abiotic reactors was primarily due to PFCAs ≤C8 (2.48 nmol/kg dry refuse). Concentrations of known biodegradation intermediates, including methylperfluorobutane sulfonamide acetic acid and the n:2 and n:3 fluorotelomer carboxylates, increased steadily after the onset of methanogenesis, with the 5:3 fluorotelomer carboxylate becoming the single most concentrated PFAS observed in live reactors (9.53 nmol/kg dry refuse).