PFAS and Water Reuse: Managing Contamination in Recycled Water Systems

The Circular Water Problem: PFAS in Recycled and Reclaimed Water

Water scarcity—driven by population growth, climate change, and aquifer depletion—is forcing water managers worldwide to embrace recycled water as an essential supplement to conventional supplies. Indirect potable reuse (IPR)—where treated wastewater is discharged to an environmental buffer like a reservoir or aquifer before withdrawal for drinking water treatment—is already practiced in dozens of U.S. cities. Direct potable reuse (DPR)—where advanced-treated wastewater is fed directly to the drinking water system—is emerging in water-scarce jurisdictions including parts of California and Texas. For all these applications, PFAS in the source wastewater creates treatment and regulatory challenges that must be resolved for recycled water programs to be both safe and publicly acceptable.

PFAS Concentrations in Municipal Wastewater

Municipal wastewater—the source material for recycled water programs—contains PFAS from multiple contributing sources: industrial dischargers to the sewer system, household product PFAS that washes off clothing and consumer products, PFAS from personal care products and household cleaners, and PFAS from food packaging degradation. Studies of wastewater influent at municipal treatment plants typically find dozens of PFAS compounds at concentrations in the range of 10 to 1,000 nanograms per liter—concentrations that, without treatment, would produce recycled water with PFAS levels potentially exceeding the EPA’s new drinking water MCLs.

Conventional biological wastewater treatment—the primary treatment in most municipal plants—does not remove PFAS effectively. Some PFAS transformation occurs during biological treatment (precursor compounds may degrade to terminal PFAS products), but the net effect of biological treatment on PFAS mass is small. Advanced treatment processes required for recycled water programs—particularly reverse osmosis (RO) and advanced oxidation—provide substantially better PFAS removal, but their deployment and cost implications must be carefully designed into water reuse facility plans.

Treatment Technologies for Recycled Water PFAS Removal

The advanced treatment train typical of potable water reuse facilities—microfiltration/ultrafiltration, reverse osmosis, UV/advanced oxidation—provides the most comprehensive PFAS removal available at utility scale. RO removes >95% of most PFAS compounds by size exclusion, while UV/advanced oxidation with persulfate or hydrogen peroxide can destroy PFAS in the RO concentrate or permeate where needed. This treatment train achieves PFAS concentrations in the final product water well below the EPA’s MCLs, supporting safe potable reuse.

For non-potable reuse applications—irrigation, industrial cooling, toilet flushing—the treatment requirements are less stringent, but PFAS accumulation in irrigated soils and exposure pathways for agricultural workers and nearby residents still require characterization. California’s framework for non-potable reuse is developing PFAS provisions that acknowledge the lower exposure risk from non-potable applications while setting protective thresholds for high-sensitivity uses like edible crop irrigation.

Public Perception and Regulatory Frameworks

PFAS in recycled water is a public communication challenge that water utilities navigating potable reuse programs must address directly. Transparent communication about PFAS removal efficiencies in advanced treatment systems, comparisons between recycled water PFAS levels and those in conventional water supplies, and honest acknowledgment of the remaining uncertainties help build the public trust that successful potable reuse programs require. Several states—including California (DPR framework), Texas, and Virginia—are developing potable reuse regulations that explicitly address PFAS, providing the regulatory clarity that utilities need to invest in appropriate treatment infrastructure with confidence in their regulatory compliance path.

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