Responding To PFAS In Wastewater Treatment

Per- and polyfluoroalkyl substances, commonly called PFAS, are a large family of synthetic chemicals used in products that resist water, grease, heat, and stains. Their strong carbon-fluorine bonds make them useful in manufacturing, yet difficult to break down in the environment. Wastewater agencies are now examining how these compounds move through collection systems, treatment plants, biosolids programs, receiving waters, and drinking water sources.

PFAS detection and treatment require a different mindset from conventional wastewater control. Standard biological processes can remove nutrients and organic matter effectively, but they generally do not destroy PFAS. Some compounds remain dissolved in the liquid stream, while others shift into primary solids, waste activated sludge, or treatment residuals.

For professionals across the Los Angeles Basin, this issue connects analytical chemistry, industrial pretreatment, source control, process engineering, residuals management, and public communication. Organizations such as LABS of CWEA provide valuable opportunities to follow technical developments and connect them with local operating experience.

Why PFAS Behave Differently

PFAS includes thousands of chemicals with different chain lengths, functional groups, and commercial uses. Perfluorooctanoic acid (PFOA) and perfluorooctanesulfonic acid (PFOS) are among the best-known compounds, but wastewater investigations may also identify shorter-chain acids, replacement chemistries, and precursor substances that transform into more persistent terminal products.

Their behavior depends on molecular structure and plant conditions. Some PFAS remain in the aqueous phase and pass through conventional treatment. Others associate with suspended solids or concentrate in sludge. Short-chain compounds are often more mobile in water and may be harder to capture with adsorption systems.

Treatment plants can therefore appear to “remove” PFAS from effluent while simply transferring part of the mass to another stream. A sound mass-balance study tracks influent, primary effluent, secondary effluent, tertiary effluent, sludge, centrate, filtrate, and final discharge. This prevents an apparent reduction in one sample location from being mistaken for destruction.

Building A Reliable Detection Program

Sampling quality is as important as instrument sensitivity. PFAS are present in many consumer and industrial materials, including some waterproof clothing, fluoropolymer components, sampling equipment, tubing, field clothing, and laboratory supplies. A careless sampling plan can create contamination or produce results that are difficult to defend.

Utilities should establish clean-sampling procedures, equipment blanks, field blanks, trip blanks where appropriate, duplicate samples, and carefully documented chain of custody. Sample containers, preservatives, holding times, and laboratory methods must align with the target analytes and regulatory purpose. Analytical reporting should distinguish between a targeted list of compounds and broader suspect-screening work.

A monitoring campaign is more useful when it answers a defined operational question. A utility may be trying to locate an industrial contributor, evaluate a landfill leachate contribution, understand biosolids loading, or establish a baseline before installing treatment. Repeated sampling during dry and wet weather can reveal whether concentrations are steady, episodic, or linked to stormwater and industrial discharge patterns.

Connecting Results To Plant Operations

PFAS data should be interpreted alongside flow, total suspended solids, organic loading, industrial discharge records, and solids production. Comparing concentrations alone can be misleading. A high concentration in a small side stream may represent less total mass than a lower concentration in a major flow. Calculating daily loads helps identify meaningful sources and treatment pathways.

Industrial pretreatment is often the most cost-effective control point. Facilities using PFAS-containing materials or managing waste streams with fluorinated compounds may need focused outreach, inventory reviews, discharge sampling, and pollution prevention measures. Sewer use ordinances and permits can support source investigations, though agencies should coordinate requirements with applicable state and federal rules.

The broader treatment picture also matters. Lessons from nutrient removal, sidestream management, and process monitoring can strengthen PFAS investigations. For example, resources on biological nutrient removal illustrate how operational data and process understanding support better decisions, even though biological nutrient removal itself is not a PFAS destruction technology.

Approach Primary mechanism Strengths Limitations
Granular activated carbon Adsorption onto porous carbon Proven for many longer-chain PFAS; adaptable to large flows Media exhaustion, replacement costs, and weaker performance for some short-chain compounds
Ion exchange Selective binding to resin High removal potential and smaller system footprint Resin management, competing ions, and residual disposal requirements
Reverse osmosis or nanofiltration Membrane separation Broad removal across many PFAS and other dissolved contaminants Produces a concentrated reject stream; energy and pretreatment needs can be significant
Foam fractionation Enrichment at an air-water interface Can reduce mass in concentrated waste streams Requires suitable chemistry and downstream management of the concentrate
Thermal or destructive processes Chemical or thermal breakdown Potential for permanent destruction when validated High energy demand, complex byproducts, and limited full-scale certainty for some matrices

Selecting Treatment For The Right Stream

No single technology is ideal for every wastewater application. Granular activated carbon and ion exchange may fit polishing applications or relatively clean, stable streams. Their performance depends on competing organic matter, suspended solids, pH, ionic strength, contact time, and the mixture of PFAS present. Pilot testing is essential before committing to a full-scale design.

Membrane systems can provide strong separation, but the concentrate must be managed responsibly. Sending a reject stream back to the headworks may simply recycle PFAS through the plant and increase loading to solids. A treatment train should account for concentrate storage, hauling, further processing, or a validated destruction step.

Emerging methods such as electrochemical oxidation, supercritical water oxidation, plasma treatment, and high-temperature processes are attracting interest because they aim to destroy rather than transfer contaminants. Their value depends on demonstrated destruction efficiency, treatment of short-chain products and precursors, energy use, air emissions, corrosion control, and the ability to verify that harmful transformation products are not formed.

Managing Biosolids And Concentrated Residuals

PFAS management does not end at the liquid discharge. When compounds accumulate in primary solids or waste biosolids, land application, composting, disposal, and thermal processing can create different exposure pathways. A utility should evaluate residuals alongside effluent, especially when influent loads are changing or a treatment process captures PFAS from water.

A residuals management plan should identify where PFAS mass is going, how concentrations vary between batches, and which receiving facilities can accept the material. Contracts and permit conditions may need updated sampling, notification, and recordkeeping provisions. Disposal decisions should be based on current requirements and site-specific risk, since federal and state policies continue to evolve.

Communication is another operational responsibility. Operators, regulators, industrial users, governing boards, and nearby communities need clear explanations of detection limits, measured concentrations, uncertainty, and the difference between removal and destruction. Technical language should be precise without overstating what a single sample or treatment test can prove.

Practical Steps For Utility Teams

A phased program helps agencies control costs while building defensible information. Start with a conceptual site model that maps potential sources, flow paths, treatment units, solids streams, and environmental receptors. Then prioritize sampling locations according to the decisions the data must support.

Teams can strengthen readiness through professional development, peer exchange, and cross-functional review. The committee activities of a regional water environment organization can connect agency staff, consultants, engineers, and operators with discussions that bridge laboratory findings and field implementation.

Recommended actions include:

These steps also support grant applications, regulatory discussions, capital planning, and public reporting. A well-organized data set can show whether source control is working, whether a treatment unit is approaching breakthrough, and whether PFAS has been transferred into a concentrated residual.

PFAS challenges will continue to develop as analytical methods improve and regulators refine expectations for drinking water, wastewater, industrial discharges, and biosolids. Water professionals can respond effectively by combining careful measurement with practical process knowledge and transparent coordination.

Explore technical programs, workshops, facility tours, and professional connections through LABS of CWEA and bring PFAS questions into conversations with colleagues across the Los Angeles Basin. Shared experience can help utilities move from uncertainty to a defensible monitoring and treatment strategy.