Evidence Brief

The Precursor Problem

Why PFAS precursors become PFOA and PFOS — and why EPA Method 1633 alone misses them.

Supports Demand #3  •  Require the TOP Assay + Method 1633A, not just EPA Method 1633

The Central Fact

PFOA and PFOS are the endpoints, not the starting materials

A large share of the PFAS in industrial and municipal wastewater is not PFOA or PFOS at the point of discharge. It is precursors — polyfluorinated compounds that transform into PFOA, PFOS, and other terminal perfluoroalkyl acids (PFAAs) once they enter the environment or a living organism.

PFOA and PFOS are the endpoints of that process. They are highly resistant to further breakdown, which is exactly why they persist and accumulate. The peer-reviewed literature is consistent on this point: precursors can be converted into longer-lived, more toxic PFAAs such as PFOA and PFOS, which then enrich in the environment and in organisms.

“Precursors can be converted into longer half-life and more toxic PFAAs, such as PFOA and PFOS — which then enrich in the environment and organisms.”

Biotransformation of perfluoroalkyl acid precursors, Environmental Pollution (Elsevier), 2020

How The Transformation Happens

Two well-documented families of precursors

Precursor → Terminal PFAA Pathway

Discharged Precursors FOSA, EtFOSA, FTOHs, FTSAs…
Transform Conversion in river, sediment, tissue
Endpoint PFOA & PFOS persistent · accumulating

Driven by: microbial degradation in activated sludge · hydrolysis · oxidation · atmospheric photolysis
These are the exact conditions inside and downstream of a wastewater treatment plant.

Pathway 01

Sulfonamide-based precursors

Perfluorooctane sulfonamide (FOSA), its N-ethyl derivatives (EtFOSA, EtFOSE), and compounds derived from perfluorooctane sulfonyl fluoride (POSF) degrade to PFOS. The research community groups all of these under one term: “PreFOS.”

→ become PFOS
Pathway 02

Fluorotelomer-based precursors

Fluorotelomer alcohols (FTOHs) and sulfonates (FTSAs) degrade into perfluoroalkyl carboxylic acids (PFCAs), including PFOA. Sulfonamides can also oxidize in the atmosphere to form PFCAs at yields reported up to ten times greater than FTOHs.

→ become PFOA / PFCAs

Why This Matters For A Discharge Permit

Monitoring only the pipe counts the problem at its lowest point

If a permit tracks only the terminal compounds (PFOA, PFOS) at the outfall, it counts the PFAS load at its smallest value — before precursors in that same discharge have finished converting into more PFOA and PFOS downstream, in the receiving water, in sediment, and in fish and human tissue.

A bioaccumulation review put the consequence plainly: the PFOS that people and wildlife are exposed to may be PFOS discharged directly, PFOS formed from precursors that transformed in the environment, or PFOS formed from precursors that transformed inside the organism after exposure. Measuring only the parent compound at the pipe understates the true eventual burden.

“Monitoring only the parent compound at the pipe understates the true eventual burden.”

The impact of precursors on aquatic exposure assessment for PFAS, PMC8359936

The Case For The TOP Assay

Why Method 1633 alone is not enough

EPA Method 1633 is a targeted method. It looks for 40 named compounds, most of them terminal PFAAs. By design, it does not quantify most precursors — because commercial analytical standards for the thousands of precursor compounds simply do not exist.

Method 1633 alone

Counts what is present today

A fixed list of 40 named compounds, predominantly terminal PFAAs. Most precursors are invisible to it. It reports the smallest, best-case version of the load.

1633A + TOP Assay

Counts what the discharge will produce

The TOP assay chemically oxidizes the sample, forcing oxidizable precursors to convert into measurable PFCAs. The rise between the pre- and post-TOP result is the hidden precursor load.

In a source-apportionment study spanning 145 samples across 46 locations and three countries, the PFAS composition from wastewater treatment plants was dominated by precursors — the very fraction Method 1633 does not capture. A 2025 study running Method 1633 alongside a TOP assay at a wastewater plant confirmed it directly: substantial unidentified precursors transformed into terminal PFCAs during the assay — mass the targeted method alone never reported.

“Commonly used targeted methods (e.g., EPA Method 537.1, EPA Method 1633) include 40 or fewer PFAS… As a result, these methods overlook most PFAA precursors.”

Selective Quantification Using the TOP Assay, Environmental Science & Technology, 2024

The Semiconductor Connection

This is specifically a fab concern

This is not a general problem that happens to apply to Micron. Semiconductor manufacturing uses a wide range of fluorinated compounds, and the analytical-methods guidance written for the industry confirms that Method 1633 targets only 40 PFAS — a fraction of what a fab wastewater stream can contain.

40 of 133

Method 1633 targets 40 compounds. Cornell identified 133 PFAS in semiconductor fab wastewater.

Jacob et al., Cornell — Environmental Science & Technology, 2021  /  PMC12371593

The Bottom Line

Measuring the smallest possible version of the problem

A permit that (1) sets no enforceable numeric limits on PFAS and (2) relies on Method 1633 alone is measuring the smallest possible version of the problem, at the single point in the pathway where the number looks best. Precursors in that same discharge will keep converting into PFOA and PFOS after the sample is taken — in the river, in Lake Ontario, in fish, and in people.

Requiring Method 1633A paired with the TOP assay is the difference between counting the PFAS that is present today and counting the PFAS the discharge will ultimately produce. That is why Demand #3 specifies both methods, not one.

Sources

Every claim traces to a primary source

  1. Biotransformation of perfluoroalkyl acid precursors from various environmental systems Environmental Pollution (Elsevier), 2020
    sciencedirect.com/science/article/abs/pii/S0269749120365970
  2. Widening the lens on PFASs: Direct human exposure to perfluoroalkyl acid precursors PMC10782884
    pmc.ncbi.nlm.nih.gov/articles/PMC10782884
  3. Fate and Transport of PFAS Interstate Technology and Regulatory Council (ITRC)
    pfas-1.itrcweb.org/…/f_and_t_508_2020Aug.pdf
  4. PFAS behavior in the environment npj Emerging Contaminants (Nature), 2026
    nature.com/articles/s44454-026-00039-z
  5. The impact of precursors on aquatic exposure assessment for PFAS PMC8359936
    pmc.ncbi.nlm.nih.gov/articles/PMC8359936
  6. Selective Quantification of Charged and Neutral Polyfluoroalkyl Substances Using the TOP Assay Environmental Science & Technology, 2024
    pubs.acs.org/doi/10.1021/acs.est.4c13837
  7. The TOP Assay as a Forensic Tool for PFAS Source Apportionment ACS ES&T Water, 2023
    pubs.acs.org/doi/10.1021/acsestwater.3c00106
  8. Assessing PFAS and Their Precursor Transformation in a Landfill Leachate-Impacted Wastewater Treatment Plant Water Environment Research (Wiley), 2025
    onlinelibrary.wiley.com/doi/10.1002/wer.70172
  9. Practical Guidance on Selecting Analytical Methods for PFAS in Semiconductor Manufacturing Wastewater PMC12371593
    pmc.ncbi.nlm.nih.gov/articles/PMC12371593

Limits first. Design second. Contract third.

The industrial treatment section of the plant has not been designed or built yet. That window is where enforceable limits — and the right test methods — still can be written in.

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