Drinking Water Utilities Switching from GAC: What Drove the Technology Decision

The Decision to Switch: Not Taken Lightly

Drinking water utilities do not replace treatment technology casually. Capital infrastructure for filtration systems represents multi-million-dollar investments with expected service lives of 20 years or more. Operational staff are trained on existing equipment. Regulatory compliance documentation is built around established processes. When utilities make the decision to replace GAC-based PFAS treatment with next-generation PFAS-selective media, the decision reflects a concrete failure of the incumbent technology to meet performance requirements — not a preference for novelty.

Interviews and case study documentation from utilities that have made this switch over the past several years reveal a consistent set of driving factors. Short-chain PFAS breakthrough at unacceptably early bed volumes is the most frequently cited technical driver. Regulatory expansion of the PFAS compound list requiring treatment — from PFOS/PFOA to the full EPA 2024 group of six — is the most frequently cited regulatory driver. And increasing transparency of PFAS monitoring data, which makes performance gaps visible to regulators and the public, creates accountability pressure that makes the status quo untenable.

Short-Chain Breakthrough: The Performance Trigger

The technical trigger for most technology switches has been the observation of short-chain PFAS — typically PFBS or PFHxA — at effluent concentrations near or above regulatory limits well before the expected end of GAC service life based on PFOS performance. This finding reveals a fundamental limitation of using PFOS breakthrough as the primary media exhaustion indicator: because PFOS adsorbs to GAC far more strongly than short-chain PFAS, GAC can appear to be performing well by PFOS standards while providing inadequate removal of short-chain compounds that are present in source water.

Several utilities have documented this pattern explicitly in public-facing reports filed with state drinking water programs. The pattern typically follows a predictable trajectory: GAC installed to address PFOS/PFOA concerns performs as expected for 24 to 36 months, monitoring is expanded to include short-chain PFAS in response to regulatory guidance updates, PFBS or PFHxA is detected at near-MCL concentrations in finished water despite continued good PFOS removal, and the utility faces a choice between more frequent GAC replacement (increasing cost) or technology change (higher upfront cost, better long-term performance).

Regulatory Expansion as a Forcing Function

The EPA 2024 NPDWR established MCLs for PFBS and PFHxS in addition to PFOA and PFOS, creating compliance obligations for compounds that many existing GAC systems cannot reliably remove to the required level. For utilities with source water containing detectable PFBS or PFHxS, this regulatory expansion did not require a change in contamination facts — only a change in what the regulatory framework required them to treat. Systems that had been compliant under PFOA/PFOS-only requirements suddenly faced compliance gaps for the newly regulated compounds.

This regulatory forcing function has driven procurement processes at dozens of utilities simultaneously, which is one reason that the market for PFAS-selective media has grown rapidly in the period following the 2024 NPDWR. Utilities in states with state-level PFAS standards that predate the federal rule have been through this experience earlier and provide a preview of the technology decision process for utilities in states where the federal MCLs represent the primary compliance driver.

Total Cost of Ownership Analysis

Utilities that have conducted rigorous total cost of ownership analysis comparing GAC replacement cycles adjusted for short-chain breakthrough with PFAS-selective media alternatives have generally found that the long-term economics favor next-generation media when short-chain compounds are present in source water. The analysis must account for GAC replacement frequency based on the earliest-exhausting regulated compound (not just PFOS), disposal costs for PFAS-laden spent GAC, and the capital cost of technology changeover.

Some utilities have found that the combination of more frequent GAC replacement required for short-chain PFAS compliance and escalating disposal costs for PFAS-laden carbon makes the ongoing operational cost of GAC-only treatment comparable to or higher than PFAS-selective media over a 10-year horizon. This finding has been influential in utility board presentations seeking approval for technology transitions, where the cost argument is often more persuasive than the performance argument alone.

Lessons for Utilities Evaluating the Decision

Utilities currently evaluating whether to maintain GAC treatment or transition to PFAS-selective media should ensure that their source water analytical panel includes all six EPA-regulated PFAS compounds, not just PFOS and PFOA. They should model GAC replacement frequency and cost based on the compound with the earliest predicted MCL breakthrough, not the compound with the longest run length. And they should obtain PFAS-selective media performance data generated with their site-specific source water chemistry rather than relying solely on clean-water isotherms.

The utilities that have completed this analysis and made the switch report that the primary benefit, beyond regulatory compliance, is predictability: PFAS-selective media shows more uniform exhaustion behavior across compound classes, making service life and replacement scheduling more reliable. In the context of a regulatory environment that is likely to require coverage of more PFAS compounds over time, that predictability is itself a significant operational asset.

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