SaveOur Bay · Independent Lab Analysis

Forever chemicals are in our bay's fish.

An independent test commissioned by the Good Samaritan Institute found 14 different PFAS in catfish pulled from a stormwater outfall in the Choctawhatchee Bay watershed — led by PFOS at levels worth everyone's attention.

Total PFAS detected · 13-catfish liver composite
0µg/kg
Sum of 14 detected compounds, wet-weight basis
0
PFOS — the dominant compound
0
PFAS compounds found
0
PFNA, second-highest
EPA 1633
Draft method, 40-analyte panel
The basics

What are "forever chemicals," and why do they end up in fish?

PFAS — per- and polyfluoroalkyl substances — are a family of thousands of synthetic chemicals prized for repelling water, grease, and stains. The same near-indestructible bond that makes them useful means they essentially never break down in nature. They wash off products and out of industrial sites, travel through stormwater and groundwater, and accumulate as they move up the food chain.

They don't break down

The carbon–fluorine bond is one of the strongest in chemistry. PFAS persist in water, soil, and bodies for years to decades — hence the nickname "forever chemicals."

They build up in living things

Long-chain PFAS like PFOS bind to proteins in blood and the liver. Predatory fish concentrate them from water and prey — so a fish's tissue is a sensitive record of what's in the water.

They affect our health

Regulators link PFAS exposure to immune, liver, thyroid, developmental, and cancer effects. In 2023 the WHO's cancer agency classified PFOA as carcinogenic to humans.

What the lab found

Thirteen catfish. Fourteen forever chemicals.

In April 2024 the Good Samaritan Institute collected 13 catfish at the Mosquito Control Ditch #10 stormwater outfall (240 Osprey Ln, Santa Rosa Beach) and sent their combined livers — a single composite sample — to Pace Analytical, a nationally accredited lab. Using the EPA's draft Method 1633, the lab detected 14 distinct PFAS compounds. These are the headline numbers — every figure here is taken directly from the lab's Report of Analysis.

0µg/kg
PFOS
68% of all PFAS in the sample
0µg/kg
PFNA
Second-highest detection
0µg/kg
Total PFAS
Sum of 14 detected compounds
0/ 40
Compounds detected
Of the EPA 1633 panel screened

Read this honestly: liver, not fillet

This is a composite of catfish livers — the organ that concentrates PFAS far more than the fillet most people eat. Because the livers of 13 fish were pooled, the result reflects the local population, not a single outlier. That makes it a powerful early-warning bioindicator of contamination in the bay — but it is not a direct measure of what's on your dinner plate. The honest takeaway: PFAS are clearly present and accumulating in this watershed's food web, and fillet-level testing plus a source investigation are the logical next steps. We flag this caveat on every benchmark comparison below.

Interactive · sourced from the lab report

Explore every detection

Each bar is a PFAS compound the lab measured above its detection limit. Tap any bar for what the chemical is, where it comes from, and its exact reported value. PFOS so dominates that a log scale helps reveal the smaller, trace-level detections.

Sulfonic acids (PFSAs) Carboxylic acids (PFCAs)
Values in micrograms per kilogram (µg/kg = parts per billion), wet weight. J = estimated, below the reporting limit.

A profile dominated by PFOS

More than two-thirds of the total PFAS burden is a single legacy compound — PFOS — the most bioaccumulative member of the family and the one most commonly found in freshwater fish nationwide. Sulfonic-acid PFAS (PFSAs) make up about 71% of the total; carboxylic acids (PFCAs) account for the rest. This "PFOS-led" fingerprint is typical of older contamination from firefighting foam, metal plating, and stain-resistant treatments.

PFSAs  68.5 µg/kg · 71% PFCAs  28.2 µg/kg · 29%
The full dataset

Every compound the lab screened

All PFAS analytes from the catfish-liver analysis — detections and non-detections alike. Sort any column, search by name, or filter to just the detections. Reporting Limit (RL) and Method Detection Limit (MDL) show how sensitive the test was for each compound.

Compound Class ▲▼ Result ▲▼ RL ▲▼ MDL ▲▼ CAS No. ▲▼
Units: µg/kg (parts per billion), wet weight · J = estimated value between the MDL and reporting limit · < = not detected above the value shown · Method: EPA 1633 (draft), Pace Analytical Services – Minneapolis.
Putting 66 µg/kg in context

How does this compare?

There is no federal limit for PFAS in fish tissue, but several states and national studies give us yardsticks. Here's where this sample's PFOS lands against them — with the essential reminder that those yardsticks are built on fillet/muscle data, while our sample is PFOS-concentrating liver.

PFOS in the catfish liver vs. fish-tissue reference points

Liver ≠ fillet — directional only
MI limited-eat · 1.5
US fillet median · 9.5
MI "Do Not Eat" · 50
This sample · 66.1 µg/kg
016.53349.566
0 µg/kg

Michigan "Do Not Eat" trigger

Michigan's 2024 PFOS threshold for a "Do Not Eat" fish advisory (fillet). Our liver value sits above it.

Verified · MI EGLE/MDHHS 2024
0 µg/kg

U.S. freshwater fillet median

Median total PFAS in 500+ U.S. freshwater fish fillets (2013–2015 EPA monitoring data, analyzed 2023).

Verified · EWG / Barbo et al. 2023
0 µg/kg

Channel-catfish muscle (national)

PFOS in channel-catfish muscle in EPA's multi-species fish dataset — a like-species, fillet-basis reference point.

Verified · EPA 823-R-24-001
0 ppt

EPA drinking-water limit (PFOS)

The enforceable PFOS limit for drinking water, for scale. Water and fish-tissue units differ — this is context, not a tissue comparison.

Verified · EPA NPDWR, 2024

Why we won't say "the catfish exceeds the Do-Not-Eat level"

Liver tissue routinely carries several times more PFAS than fillet from the same fish. A clean apples-to-apples comparison needs a fillet sample. What this liver result does establish is that PFAS are present and bioaccumulating in the watershed at levels that warrant follow-up fillet testing and a hunt for the source.

Why it matters for people

What PFAS exposure does to health

These are the health effects U.S. agencies (EPA, ATSDR) associate with the PFAS family at sufficient exposure. The catfish itself isn't the only concern — the same chemicals reach people through drinking water, other foods, and consumer products.

Heart & cholesterol

Linked to increased cholesterol and pregnancy-induced high blood pressure.

Liver damage

Associated with elevated liver enzymes and altered liver function.

Immune & thyroid

Reduced vaccine response in children; disrupted thyroid hormones.

Development & cancer

Lower birth weights; kidney and testicular cancer associations.

WHO / IARC · 2023

PFOA — Group 1

"Carcinogenic to humans" — the agency's highest certainty class. Detected here at 0.96 µg/kg.

1
WHO / IARC · 2023

PFOS — Group 2B

"Possibly carcinogenic to humans." It's the dominant compound in this sample at 66.1 µg/kg.

2B

Verified  Health associations per U.S. EPA and ATSDR toxicological profiles; cancer classifications per IARC Monographs Vol. 135 (Nov 2023). These describe the PFAS family and named compounds in general — not a clinical assessment of risk from this specific fish.

A live policy window

Two of the chemicals in this fish are about to lose federal protection

In May 2026 the EPA proposed rescinding drinking-water regulatory determinations for several PFAS — including PFNA and PFHxS, both detected in this catfish (PFNA is the second-highest result here). The public comment window is open now.

Public comment is open until July 20, 2026

The EPA is also proposing to extend PFOA/PFOS compliance deadlines to 2031. For a coastal special district working on stormwater and source-water protection, this is the moment to put watershed evidence — like this analysis — on the record. A virtual public hearing is set for July 7, 2026.

Jul 20
2026 · comment deadline

Verified  EPA proposed rules, Federal Register, May 2026 (PFAS Rescission Rule; PFOA/PFOS Compliance Extension Rule). Status as of late June 2026 — confirm current docket dates before filing.

Provenance & rigor

How the test was done

Credible numbers depend on a credible chain of custody. Here's exactly how the sample was collected, analyzed, and quality-checked — drawn from the lab's full Report of Analysis, which you can download below.

Sample & method
Sample
Composite livers, 13 catfish (tissue)
Collected
April 16, 2024
Collection site
Mosquito Control Ditch #10 outfall — 240 Osprey Ln, Santa Rosa Beach, FL 32459
Watershed
Drains to Choctawhatchee Bay system
Analytical method
EPA 1633 (draft) — LC-MS/MS
Basis
Wet weight · 2.121 g aliquot
Project / Lot
PFAS Biota & Soil · ZD17009
Pace project no.
10689691

The fish were taken at a stormwater outfall — Mosquito Control Ditch #10 — which channels runoff into the watershed. That makes the site a logical place to look for a PFAS source. EPA Method 1633 is the agency's draft single-laboratory–validated procedure for 40 PFAS in water, soil, biosolids, and tissue, using isotope-dilution liquid chromatography–tandem mass spectrometry — the current gold standard for PFAS quantitation.

Laboratory & accreditation

Pace Analytical Services, LLC — a nationally accredited environmental laboratory network. Sample preparation (grinding) was performed at Pace's Green Bay, WI facility; PFAS analysis at Pace's Minneapolis, MN laboratory. The receiving lab (Pace West Columbia, SC, formerly Shealy Environmental) holds Florida certification #E87605/E87653.

Accreditation includes TNI/NELAP, DoD ELAP (A2LA #2926.01), ISO/IEC 17025, and a Federal Fish & Wildlife permit for biological-tissue handling — the credentials that make the results defensible in a regulatory setting.

Quality control — did the numbers hold up?

Method blanks were clean for every key detection (PFOS, PFNA, PFDA and the rest read below their reporting limits in the blank) — so the compounds found in the fish came from the fish, not the lab. Samples were analyzed within method hold times, and isotope-labeled surrogates were carried through to track recovery.

A few quality flags appear in the report and are disclosed here for transparency: some fluorotelomer-sulfonate surrogates fell outside control limits (S0), and two analytes that were not detected had control-sample recoveries outside limits (L1/L2). None of these affect the primary PFOS/PFNA/PFDA detections that drive this story.

J — estimated; above MDL, below reporting limit L1 — lab-control recovery above limits (non-detect analytes) L2 — lab-control recovery below limits (non-detect analytes) S0 — surrogate recovery outside control limits
Resources

Read the source — and the science

Everything on this page traces back to the primary lab report. Download the full 31-page Report of Analysis, and follow the references behind every benchmark and health claim.

PDF

Full Report of Analysis

The complete, unaltered Pace Analytical report — case narrative, certifications, full analytical results, quality-control data, and chain of custody.

31 pagesPDF · 4.1 MB
Lot ZD17009Pace No. 10689691
May 21, 2024Date completed
Download the PDF
Get involved

Clean water is a community project.

The Good Samaritan Institute commissioned this analysis to put real watershed data in front of the people and agencies who can act on it. Share it, test further, and add your voice while the federal comment window is open.