The Duck Chugger

The Duck Chugger · Field Science

On Eating Contaminated Ducks

Two studies, one year apart, force a hunter to ask two very different questions. The first — from the Northeast — is the familiar one: which species, how often, prepared how. The second — from a lake in New Mexico — throws it out entirely. The full story, with every chart live and pokeable.

This is the full article with live charts. Every figure below is interactive — flip data sets, preparations, and thresholds yourself. Prefer a quieter read? The same essay runs on Substack with static images.

Read it on Substack →

The article · read it through

The charts · jump to any figure

Data, code & reproducibility

This isn’t pearl-clutching, or telling you to eat fewer ducks, or do anything at all. I’m just a curious person who wanted to look into this more after a recent blurb in the Delta Waterfowl magazine. Despite the alarming raw numbers, the average duck you eat probably isn’t all that much worse than other meat on your table.

First, a disclaimer

I am not a scientist, I am a data nerd with high speed internet access. I am curious about the contents of the ducks we all harvest and eat and went looking for answers. Nothing below should be taken as advice, but rather just some insight into what I found already published on the subject and my own plans for eating my birds. I will still probably eat a number quite a bit greater than what is likely to be completely safe.

For the past few years I’ve paid increasing attention to duck activity in marginal spaces around my home — wastewater plants, landfill waste ponds, and similar environments — and have wondered exactly what they were eating, how that may affect their contamination rates & how much of that contamination makes its way onto my plate. Fortunately, a number of researchers across the country have answered that question for me and the results, while surprising, might suggest something much larger about the health risks of our current food system than perhaps anything else.

The gist on ducks: it’s usually about where the duck was shot. For the overwhelming majority of birds — pulled out of natural marshes and ag areas — waterfowl is a low-risk protein that could have contamination further reduced by skinning and cooking. But a small number of birds are significantly contaminated from the surrounding environment, and for those, no amount of trimming, cooking, or species-picking will reduce the contamination levels to a safe threshold for human consumption.

Before you read a single number: what “cancer risk” here does and doesn’t mean

The “added lifetime cancer risk” on this page is a regulatory construct, not a diagnosis. It comes from EPA’s linear low-dose model, where each contaminant’s slope factor is derived from a specific tumor type in a specific study — PFOS’s from liver and pancreatic tumors, dioxin’s from a different set, and so on. “Cancer” is not one disease, and these numbers are not universally translatable: an exposure that nudges one organ’s risk tells you nothing about the dozens of other cancers that make up the baseline.

So when we say a habit “adds 1 in N” on top of the ~40% lifetime baseline (which is all cancers combined, per the American Cancer Society), treat it as an order-of-magnitude yardstick for comparison — the honest way to line a duck up against another food source — not a literal statement that your personal risk of every cancer rises by that amount. Summing several contaminants into one number is a standard but conservative simplification, and individual susceptibility, age, and genetics all move the real figure. This is a risk explainer, not medical advice.

Regime 1The baseline bird

In January 2025, a team led by Cornell’s Wildlife Health Lab published the best modern baseline we have. They collected 108 wild ducks and geese from hunters across New York, Pennsylvania, Connecticut, and New Jersey and ran the breast meat of five species — Canada goose, wood duck, American black duck, green-winged teal, and mallard — through a battery of tests for mercury, dioxins, PCBs, banned pesticides, and PFAS. Then they ran two EPA-standard risk assessments: a non-cancer hazard index (anything under 1.0 is considered safe) and an excess lifetime cancer risk, on raw meat with the skin and fat left on — the most contaminated way you could prepare a bird.

Three things fall out of their data, and they’re the practical core of everyday duck hunting.

Species is the biggest lever. Canada geese and wood ducks — grazers and perching ducks that spend less time nose-down in contaminated sediment — carried the lowest burdens and are clean enough to eat weekly. Black ducks and green-winged teal are about a once-a-month bird. Mallards were the dirtiest of the five, closer to twice a month at most. My assumption is that this is due to differences in diet and thus contaminant uptake rates. You can see the whole study as one grid — every species against every eating frequency, shaded by regulatory band — in the master grid just below. Flip to any hotspot and the story changes — all of those birds are wildly contaminated.

Preparation is the second lever, and it’s nearly free. The contaminants that drive the cancer numbers — dioxins, PCBs, legacy pesticides — are fat-soluble. They ride in the skin and yellow subcutaneous fat, not the lean red muscle. Skinning and trimming removes roughly half of them; cooking so the fat renders and drips removes about a third; doing both lands around a two-thirds reduction, which effectively doubles how many meals a month you can safely eat. (Mercury is the exception — it binds to muscle protein, so trimming and cooking don’t touch it — but mercury doesn’t drive cancer risk.) The preparation chart turns this into meals-per-month you actually gain.

Keep perspective. Put a once-a-month serving of each bird on the same ruler as everything else people eat, and the ducks are unremarkable. Every one of them sits below a daily glass of wine or a daily strip of bacon, and the cleanest land near a monthly serving of store-bought salmon — see the risk ladder. Even eating the dirtiest of these birds every single day for life raises your lifetime cancer chance by under half a percent, against the ~40% baseline every human already carries. And the cancer risk is shared three ways: two legacy pollutants — dioxins and PCBs — plus PFOS, once you apply the slope factor the study couldn’t (more on that just below). For the cleanest birds, goose and wood duck, PFOS is actually the single biggest contributor. The catch is that trimming and cooking strip the fat-soluble dioxins and PCBs but not PFOS, which rides in the lean muscle and stays put. That composition is the drivers chart.

The fear, defused. The scariest way to state a risk is as a multiplier — but to double your lifetime cancer risk, an exposure would need a multiplier of 2.0, and a lifetime of eating even the dirtiest of these birds every single day comes to about 1.005. Picture a stadium of 10,000 people: about 4,000 develop cancer no matter what they eat. At an everyday-for-life pace the cleanest species add roughly one extra case, the dirtiest a dozen or two — dwarfed by the ~120–130 that a daily drink or daily bacon habit piles on; at a realistic once-a-month pace the birds’ extra cases nearly vanish. Fill the stadium yourself.

If every duck lived in Regime 1, the charts below would be the end of the article, and the cheat sheet — safe meals per month, by species and preparation — would be all you needed to print. Read them, play with them — then comes the twist.

Data set — flips every per-species chart (01–04) between the Northeastern background and a measured PFAS hotspot (Green Bay, Minnesota, or Holloman)
Preparation — strips fat-soluble contaminants only (does nothing to a hotspot’s PFOS). Also sets how the Northeastern birds are prepared in the stadium (05).
These settings drive every chart tagged ▲ Chart controls below — including the stadium, even though it has its own bird buttons.
01▲ Chart controls · data set & preparation

Each cell is the added lifetime chance of cancer from eating that species at that frequency, for life — written as “1 in N” and shaded by regulatory band. Rows sort cleanest bird on top. Flip the preparation toggle above and watch the grid cool off.

The master grid: added lifetime cancer risk by species & frequency

Negligible (< 1 in a million) Level of concern Action threshold (> 1 in 10,000)
“1 in N” = one extra case per N people who eat that way for a lifetime, on top of the ~4,000-in-10,000 who get cancer regardless. Population-average (mean) birds.
02▲ Chart controls · data set & preparation

The five birds — eaten once a month — dropped onto the same log-scale ruler as everyday foods and habits. Teal-green dots are the ducks; chestnut dots are food & lifestyle comparisons.

The risk ladder: a monthly duck vs. everyday foods

Everyday foods that outrank a duck

The ladder puts a monthly duck against a few anchors; here it is as a plain list. Each item below is a common food or drink that mainstream cancer science treats as riskier than eating an ordinary (Regime 1) duck once a month — with one honest catch: these are things people eat every day, while the duck is monthly. The odds are added lifetime cancer risk on the same “1 in N” scale, and — exactly as the disclaimer up top warns — they’re organ-specific conversions (colorectal for meat; several sites for alcohol), not one universal cancer number.

Food & typical habitIARC class Added lifetime riskMain cancer site(s)
Processed meat — ~2 slices of bacon or 1 hot dog, every day Group 1 — carcinogenic to humans ~1 in 80colorectal
Alcohol — one drink, every day Group 1 — carcinogenic to humans ~1 in 85breast, liver, colorectal, mouth & throat
Red meat — ~100 g beef/pork/lamb, every day Group 2A — probably carcinogenic ~1 in 130colorectal
Charred / well-done grilled meat — regularly (HCAs & PAHs) Group 2A components elevated*colorectal, stomach, pancreas
Salt-preserved fish & heavily salted foods — regularly Group 1 (Cantonese-style salted fish) elevated*nasopharyngeal, stomach
“1 in N” = one extra lifetime case per N people with that daily habit, on top of the ~40% baseline. Meat and alcohol figures convert IARC/WCRF relative risks (processed meat +18% and red meat +17% colorectal per 50–100 g/day; alcohol across several sites) to absolute lifetime risk using U.S. organ-specific baselines; bacon and alcohol match the anchors on the ladder above. *“Elevated” = a recognized increase that isn’t cleanly reducible to a single number. Sources: IARC Monographs (2015, processed & red meat; 2012/2010, alcohol & salted fish), WCRF/AICR.

To put waterfowl on the exact same daily-for-life basis as the foods above, here is the whole span — from the cleanest ordinary bird you could eat every day to the single worst bird from the country’s hottest PFAS site:

The waterfowl bracket — eaten every day, for life

Best case · cleanest bird
~1 in 6,400
Canada goose, skinned & cooked, eaten every day for life (~1 in 4,200 as-shot, skin-on). Cleaner than every food on the list — roughly 80× below daily bacon.
Average · typical bird
~1 in 990
Average of the five study species, skin-on, eaten every day for life (~1 in 1,800 skinned & cooked). Still safer than a daily drink or bacon — and this is the daily pace; a monthly duck is ~30× lower.
Worst case · hotspot bird
off the scale
American wigeon from Holloman Lake, eaten every day: the linear model returns ~1 in 1, which is so far past its valid range it isn’t a real probability — it simply reads “do not eat.” This is the site, not the species.
Same daily-for-life yardstick as the food table. Best case = cleanest Northeastern study bird at its best preparation; average = the mean across all five study species (skin-on); worst = the dirtiest measured Holloman bird (PFOS in muscle modeled 0.2× liver). The gap from left to right is the entire point of this piece: an ordinary duck — clean or average — is one of the safer proteins you can eat, and a hotspot duck is one of the worst — and where the bird fed decides which one you have.

For scale: a once-a-month ordinary duck runs from about 1 in 130,000 (Canada goose) to 1 in 12,000 (mallard) on this exact scale — so even the dirtiest Regime 1 bird, eaten monthly, sits hundreds to thousands of times below a daily bacon, drink, or red-meat habit (and those figures are skin-on and raw; trim and cook and the duck improves further). None of this makes bacon a crisis — it makes the point that a clean wild duck is one of the lower-risk proteins on the table. The one place this flips is a PFAS hotspot, which is the rest of this piece.

03▲ Chart controls · data set

The lever hunters actually control — for Northeastern study birds. The contaminants that drive their cancer risk hide in skin and fat, so skinning, trimming, and cooking removes roughly half — up to two-thirds — of them; longer bar = more meals a month. Now flip the data set to a hotspot (Green Bay, Minnesota, or Holloman) and the lever dies: PFOS rides in the lean meat, so every preparation lands at the same place.

What trimming & cooking buys you, by species

Safe meals per month (typical bird) under each of the four preparations.

“Safe” is set by the stricter non-cancer hazard limit. New York’s blanket 2-meals-a-month advisory is marked for reference. Mercury is unaffected by preparation, so gains are real but bounded.
04▲ Chart controls · data set

For Northeastern study birds, three families share the cancer risk: two legacy pollutants banned decades ago — dioxins and PCBs — and PFOS, once you apply the slope factor the study lacked. For the cleanest species (goose, wood duck) PFOS is already the single biggest contributor. Flip to any hotspot (Green Bay, Minnesota, Holloman) and the sharing stops: the cancer risk is essentially all PFOS.

What drives each species’ cancer risk

Share of the average bird’s added cancer risk, by contaminant family (skin-on, raw).

Dioxin share is deliberately conservative (borderline detections counted as positives); the true dioxin share — and the totals throughout — is likely lower.
05▲ Chart controls · preparation · + pick any bird below

The antidote to scary multipliers. Fill a stadium with 10,000 people; the grey blocks are the ~4,000 who develop cancer no matter what. Pick a bird — a Northeastern study bird, a hotspot bird (Green Bay, Minnesota, or Holloman), or bacon/wine — and see the extra cases. Northeastern birds and foods are eaten every day, for life; watch a single hotspot duck a month dwarf a daily bacon habit.

A stadium of 10,000 people

Sage = the ~4,000 who develop cancer anyway. The coloured cluster (ringed) is the extra cases, and its colour marks the regulatory band. Faint gridlines divide the crowd into 100 blocks of 100 people. The buttons below only pick which bird fills the stadium — the preparation for Northeastern birds still comes from the Chart controls above.

Baseline cancer (~4,000 of 10,000) Extra · negligible Extra · level of concern Extra · action threshold
Northeastern study birds respond to the preparation toggle and are shown every day, for life; hotspot birds (Green Bay, Minnesota, Holloman) are shown once a month; bacon and wine are fixed, for scale. Even the worst Northeastern bird is a fraction of what a daily drink piles on — and the gradient across hotspots is stark: a Green Bay upper-bay mallard adds well under one case, while a Holloman bird eaten just once a month lands far past all of them (and past the linear model, i.e. “do not eat”).

The other axis: what “non-cancer risk” actually is

Cancer gets the headlines, but for these birds it’s usually not the binding constraint. The study ran a second, separate assessment — the hazard index — and it’s the one that actually sets the “safe meals per month” in the cheat sheet below.

Here’s the idea. For each contaminant, regulators publish a reference dose: the amount you could eat every day for a lifetime with no expected harm. Divide your actual intake by that reference dose and you get a hazard quotient; add the quotients across every contaminant in the meat and you get the hazard index (HI). An HI under 1.0 means you’re inside the safety envelope; over 1.0 means you’ve crossed it. Crucially, this is a margin-of-safety flag, not a probability — an HI of 5 doesn’t mean a 5-in-something chance of anything; it means five times the intake considered acceptable, which is a signal to eat less, not a diagnosis.

What are the actual health effects behind that number? They’re specific, and they’re mostly not cancer — which is exactly why the two axes don’t collapse into one:

  • Methylmercury — the nervous system. Developmental neurotoxicity is the driving concern: it crosses the placenta and affects fetal and early-childhood brain development, which is why advisories single out people who are or may become pregnant, and young children. In adults, high chronic intake brings neurological effects. Mercury binds to muscle protein, so trimming and cooking do not remove it — and in Western birds it’s often the effect that sets the limit.
  • PFOS & other PFAS — immune, liver, hormonal, developmental. EPA’s critical effect is suppression of the immune response (measurably lower antibody production after childhood vaccines). Add elevated cholesterol, liver-enzyme and thyroid changes, kidney and testicular signals, and reduced infant birth weight. The reference dose is extraordinarily low (PFOS: 1×10⁻⁷ mg/kg/day), so even modest concentrations push the hazard index up — and because PFOS rides in lean muscle, preparation can’t touch it.
  • Dioxins & dioxin-like PCBs — developmental, reproductive, endocrine, and immune effects (chloracne at high doses); scored together as toxic-equivalents (TCDD-TEQ). These are fat-soluble, so skinning, trimming, and cooking genuinely reduce them.
  • Legacy organochlorine pesticides — liver, neurological, and endocrine effects; also fat-soluble and reducible by preparation.

Two practical takeaways. First, because the hazard index reaches 1.0 before the cancer risk reaches EPA’s action threshold for these birds, the non-cancer number is what governs the cheat sheet — so the “safe meals” figures already bake in mercury and PFOS, not just cancer. Second, the people most affected by the non-cancer endpoints — pregnant and nursing women, and children — should treat every number here as a ceiling to stay well under, not a target.

06Interactive · filter it yourself

If you save one thing, save this — but set your own rules. Pick the place (the Northeast background, or a measured PFAS hotspot — Green Bay, Minnesota, or Holloman), whether your limit is governed by cancer or the non-cancer hazard, and how strict a lifetime cancer risk you’ll accept (1 in 10,000 vs. a ten×-stricter 1 in 100,000). The table recomputes safe meals per month.

Location
Limit set by
Acceptable cancer risk
Estimate
Species

Safe meals per month — interactive

 

The plot twistA slope factor the study couldn’t use

Buried in the Dayan paper’s limitations is a sentence that turns out to matter enormously:

“our estimation of cancer risk from PFAS may be especially low, as [cancer slope factor] values were not available for any PFAS except PFOA at the time of writing… should [health guidance values] become available after this writing… our PFAS data may warrant updated analysis.”

First, a quick disambiguation, because it’s the crux of the whole thing. PFAS is the family — thousands of “forever chemicals.” PFOS is its single most notorious member. They aren’t two different things being compared; PFOS is a PFAS, and in waterfowl it’s the one that matters. The Dayan team detected PFOS in 95.3% of their New York birds — the most of any PFAS they measured — while PFOA, the one compound that happened to have a cancer slope factor back then, turned up in only about a quarter. The New Mexico report tells the same story from the other extreme: across its birds, PFOS is the dominant congener. So both studies very much “said something about PFOS” — it’s the needle every measurement lands on.

To turn a concentration into a cancer number you need a slope factor — a dose-to-risk conversion — and when the paper was written, PFOS had none; only PFOA did. So the compound that dominates the birds drove the study’s non-cancer hazard but contributed exactly zero to its cancer estimate. That’s the gap the authors flagged.

In April 2024, the EPA finalized exactly the missing piece: an oral cancer slope factor for PFOS (39.5 per mg/kg/day) and a reference dose (1×10⁻⁷ mg/kg/day). The authors told us what to do when that happened — so let’s do it twice: first to their own ordinary birds, then to the place that makes it unmissable.

Start with the ordinary birds. Dayan reports PFOS right there in Table 2 — in breast muscle, the part you actually eat — averaging 3.08 ng/g across all 107 birds, ranging by species from about 1.0 in geese and wood ducks to 6.0 in mallards. Run those through the EPA slope factor with the study’s identical intake model (a 227-gram meal, an 80-kilogram adult, a lifetime of eating) and the “rounding error” evaporates: at a twice-a-month habit PFOS adds roughly a 1-in-44,000 lifetime cancer risk for an average bird — larger than the entire dioxin-and-PCB total for the cleanest species. PFOS doesn’t just belong in the background cancer math; for goose and wood duck it’s the single biggest piece of it, and because it sits in muscle rather than fat it’s the one driver trimming and cooking can’t reduce — the driver flip below splits each bird’s cancer risk into the part you can trim away and the locked-in PFOS you can’t. That alone reframes Regime 1. Now watch what the same slope factor does somewhere PFOS isn’t measured in single digits.

Regime 2The hotspot

In the desert outside Alamogordo, New Mexico, sits Holloman Lake — a body of water fed for decades by runoff from firefighting foam (AFFF) at the adjacent Air Force base. In 2025 the New Mexico Environment Department published an ecological survey of the lake, and the waterfowl numbers are unlike anything in the Dayan study. Not a little higher. Thousands of times higher.

Start with raw concentration, before any risk math. On the contamination gradient below, grocery chicken, pork, and beef form a near-zero floor around a quarter to half a nanogram of PFOS per gram — 95–99% of samples are outright non-detect (USDA’s national residue program, 2019–2023). Locally caught wild fish sit a step up, a few to ~16 ng/g. New Mexico’s statewide waterfowl — birds nowhere near the lake — already run 100 to 1,000 ng/g. And the Holloman birds themselves? Green-winged teal liver at 20,000 ng/g. American wigeon at 38,000. That’s four to five orders of magnitude above the grocery floor.

★ PFASConcentration, not risk

Before the risk math, the raw ingredient: how much PFOS is actually in things. This is the contamination gradient across the food supply on a log scale — from the near-zero floor of grocery meat and background ducks (~0.4–3 ng/g, below Wisconsin’s 1-meal-a-month line), up through contaminated-site ducks whose breast muscle — the part you eat, measured at Green Bay, Lake Elmo (MN), and Holloman — runs from “do not eat” into the low thousands, all the way to a Holloman liver bird four to five orders of magnitude above the floor.

The contamination gradient: PFOS across the food supply

Typical PFOS concentration, ng/g wet weight, log scale. Each point labeled with the tissue measured; gold/red dashed lines are Wisconsin’s muscle consumption thresholds.

The breast-muscle points are the key addition: three independent studies measured PFOS in the cut hunters eat — Green Bay mallards (up to ~480 ng/g), Minnesota’s Lake Elmo mallards (median ~950 ng/g; the same lake’s Canada geese sat far lower at ~31, a diet effect), and Holloman waterfowl (mean ~1,900 ng/g). Note Holloman’s measured muscle mean (1,903) is ~0.21× its liver mean (9,154) — almost exactly the 0.2× assumed in the risk model. Gold/red dashed lines are Wisconsin’s muscle advisory triggers (10 = 1 meal/month; 40 = do not eat); grey lines are avian egg-yolk effect levels (Newsted 2005). Sources: USDA FSIS 2019–23, EPA, Dayan 2025, Eifert/Strom 2025, LaSharr & Carstensen (MN DNR) 2024, Witt 2024, NMED 2025.

Now the risk math the original study couldn’t do. Modeled on the same excess-lifetime-cancer axis as the ordinary birds, a Holloman bird is off the top of the chart — see the hotspot dropped onto the same ruler below:

  • Eating a Holloman green-winged teal just once a year, for life, works out to roughly 1 in 810 added lifetime cancer risk — about 40 times the risk of eating an ordinary teal every month, and squarely in the EPA’s “unacceptable” band all by itself.
  • At once a month, the number blows past 1 in 100 — so far past the “action” threshold that the linear model behind it stops being a literal probability and simply reads do not eat.
  • The non-cancer hazard index at any regular pace runs into the thousands (a hazard index over 1 is the concern threshold). That, more than any cancer figure, is what puts these birds off-limits.

One assumption, stated plainly, because it’s the load-bearing one. Holloman’s headline numbers are liver, and hunters eat breast. PFOS concentrates in liver, blood, and kidney — not fat or muscle — so breast meat runs lower. I modeled muscle at 0.2× the measured liver level (a stated assumption; a 0.1–0.3× range is computed too), and I let PFOS carry the cancer number because it’s the one that’s measured, dominant, and now has a slope factor. Even at the optimistic end of that range, the birds are far past any threshold. And of note: because PFOS lives in the lean meat rather than the fat, the trim-and-cook trick that can reduce contam in Regime 1 does essentially nothing here.

★ HOTSPOTIt’s the place, not the duck

Everything above this point is the background regime — ordinary wetlands, legacy pollutants, a “which bird, how often” question. This is the other world: birds from a PFAS contamination hotspot (Holloman Lake, New Mexico), dropped onto the very same ruler. Here the question stops being which duck and becomes where was it shot.

The same ruler, two worlds: background ducks vs. a contamination hotspot

Background ducks (Dayan, once a month) Food & lifestyle anchors Holloman hotspot (one meal per year)

And it isn’t just a modeling assumption — someone measured the muscle. A thousand miles away in Green Bay, Wisconsin, state biologists did the experiment I had to approximate: they sampled PFOS directly in mallard breast muscle — the exact cut a hunter eats — from 2022 through 2024 (the work Sean Strom of the Wisconsin DNR walked through on a 2025 Delta Waterfowl podcast, and published as Eifert, Gorski, Magee & Strom, 2025). At an unimpacted reference site the birds were essentially clean — only two had any detectable PFOS at all. In Green Bay, 67% to over 90% of mallards were contaminated, running up to about 480 ng/g in the lower bay. That was high enough that in September 2025 Wisconsin issued its own waterfowl advisory: do not eat mallards from lower Green Bay, and one meal a month for mallards (one a week for wood ducks) in the upper bay. Different flyway (Mississippi, not Central), different source (industrial legacy, not a single foam pit), and — crucially — muscle, not liver: hard confirmation that hotspot PFOS reaches the meat on the plate, and that no amount of trimming rescues you. Those Green Bay points, and Wisconsin’s 10- and 40-ng/g muscle advisory thresholds, are marked on the contamination gradient — and the background Northeastern ducks sit just below the one-meal-a-month line, which is exactly why they’re a Regime 1 story.

Minnesota found the same thing — plus a twist about species. A Minnesota DNR pilot (LaSharr & Carstensen, 2024) sampled mallards and Canada geese at a long-contaminated lake (Lake Elmo, downstream of decades of PFAS manufacturing waste) and at a clean control. Control mallard breast muscle was essentially spotless — a median of 0.4 ng/g PFOS. At Lake Elmo, mallard breast muscle ran a median 948 ng/g (up to 1,400), 360 to 7,000 times the control. But the Canada geese at the very same lake sat far lower — a median 31 ng/g. Diet is why: mallards dabble in contaminated water and sediment, geese mostly graze grass. It’s the whole thesis in one lake — the place, the species, and the tissue seem to matter the most in regard to contam rates. And there’s a bonus buried in that paper: it reports the Holloman birds’ directly-measured muscle — mean 1,903 ng/g against a liver mean of 9,154 (Witt 2024), a ratio of ~0.21 that lands almost exactly on the 0.2× breast-to-liver figure I had to assume above. The load-bearing assumption checks out against real data.

That reversal is the single most important idea in this piece, and it has its own picture just below: how much of the risk you can trim away. For a Northeastern study bird, about three-quarters of the contaminant-cancer risk is fat-soluble — the dioxins and PCBs that skinning, trimming, and cooking cut into — leaving PFOS as the locked-in remainder. For a hotspot bird there is nothing to trim away: the cancer risk is essentially all PFOS, and it’s sitting in the part of the animal you actually eat.

★ PFASThe flip

The one question a hunter can act on: how much of the cancer risk can you trim away? The fat-soluble contaminants (dioxins, PCBs, pesticides) sit in skin and fat, so skinning, trimming, and cooking cut into them. PFOS does not — it’s protein-bound, riding in the lean muscle, so no preparation touches it. This chart splits each bird’s cancer risk into the part you can reduce and the part that’s locked in.

How much of the cancer risk can you trim away?

Each bar is one bird’s added cancer risk, split into what preparation can reduce (fat-soluble) vs. what it can’t (PFOS, in the muscle). Northeastern study bird vs. a Holloman bird.

“Reducible” means the portion trimming and cooking can cut (by roughly a third to two-thirds, not to zero); “locked in” is PFOS, which they can’t move at all. For a Northeastern bird about three-quarters of the contaminant-cancer risk is reducible; for a Holloman bird the cancer risk is essentially all PFOS, so preparation buys you almost nothing. The Northeastern PFOS share uses the authors’ own measured breast-muscle PFOS and EPA’s April-2024 slope factor; the Holloman bar reflects the PFOS-only hotspot model. Mercury, where present, is also locked in (it drives the non-cancer limit).

Why it’s the place, not the duck

None of this is really about ducks; it’s about their habitat. It’s a story about a few specific pieces of ground being poisoned, and migratory birds acting as the messenger. Holloman is closed to hunting — but it’s a migratory stopover, so those same birds are legally harvested hundreds of miles away, carrying their body burden with them. New Mexico’s report explicitly calls for expanded statewide testing of waterfowl and large game.

And this isn’t hypothetical or confined to one lake. Wildlife agencies have already issued wild-game “do not eat” advisories in state after state — see the advisory tracker below — and they trace to two recurring point sources:

  • Military firefighting foam (AFFF): Holloman Lake (NM); Oscoda Township, Michigan, home to the first “do not eat” deer advisory in the U.S. (2018); Marinette, Wisconsin.
  • PFAS-laden sludge spread as farm fertilizer: Fairfield, Maine, where a ~25-square-mile deer advisory traces to biosolid fertilizer (now banned in the state).
  • Industrial legacy in the water: the Green Bay, Wisconsin duck advisory above — the one hotspot on this list where the contaminant was measured straight from the breast muscle, not the liver.

Michigan and New Hampshire go further and warn against eating the organs — liver and kidney — of any wild game, precisely because that’s where PFAS concentrates.

★ PFASAlready happening

This isn’t hypothetical. Wildlife agencies have already issued wild-game “do not eat” advisories in multiple states — and they trace back to two point sources: military firefighting foam and PFAS-laden sludge spread as farm fertilizer.

Where wild game is already “do not eat” — and why

U.S. wild-game PFAS advisories by year, colored by contamination source.

A selected, non-exhaustive set of advisories. Most name deer; New Mexico’s is the waterfowl case, where hunting is closed at Holloman Lake but the birds are migratory and harvested elsewhere. Sources: state wildlife/health agencies via AP reporting (2022, 2025).

So which regime is your duck in?

For most hunters, most of the time, the honest answer is Regime 1: your birds came from ordinary wetlands, and the cheat sheet is the whole game — pick a species, pick a preparation, eat within the number, skin and trim and cook, and enjoy one of the more honest proteins you can put on a plate. Grocery meat, if you ever want the comparison, is a genuinely near-zero PFAS floor.

Treat a bird as Regime 2 — and check your state’s advisories before eating it at all — if it came from:

  • Water near a military base, airport, or fire-training area (AFFF sources).
  • Land downstream of industrial discharge or fields fertilized with municipal biosolids/sludge.
  • Any water under an existing PFAS advisory for fish or game.

When in doubt in a suspect area, two rules travel well: skip the organs entirely (PFAS loves liver and kidney), and remember that trimming and cooking — your best friends in Regime 1 — do not rescue you from PFOS in Regime 2.

Every flyway has its own hotspots. Holloman is in the Central Flyway, but this isn’t regional bad luck — it’s infrastructure. North America drains into four great migration corridors — the Pacific, Central, Mississippi, and Atlantic flyways — and every one is dotted with the same point source that poisoned Holloman: military airfields that trained for decades with AFFF firefighting foam. The Pentagon is now assessing 723 installations nationwide for PFAS; 352 have public coordinates, and mapped by flyway they number in the hundreds in each corridor — roughly 147 in the Pacific, 99 in the Central, 166 in the Mississippi, and 241 in the Atlantic (the remainder in Alaska, Hawaii, and the territories). The Environmental Working Group separately maps ~720 military AFFF sites among more than 9,700 contaminated U.S. locations. And a migrating bird doesn’t read fence lines.

★ PFASIt’s the place

Holloman sits in the Central Flyway — and it is one of hundreds. North America drains into four great migration corridors — the Pacific, Central, Mississippi, and Atlantic flyways — and the Pentagon is assessing 723 military installations for the very point source that poisoned Holloman: decades of training with AFFF firefighting foam. They sit in every flyway. A migrating duck doesn’t read fence lines.

PFAS-assessment military sites across the four flyways

Lower-48 states shaded by USFWS administrative flyway; dots are DoD PFAS-assessment installations with public coordinates. Most-affected states labeled with their totals.

States are coloured by their USFWS administrative flyway (whole-state assignment). Dots are the 352 of 723 DoD PFAS-assessment installations with public coordinates; the 326 in the lower 48 are drawn. The per-flyway tally counts all 723 (including Alaska, Hawaii and territories, which aren’t drawn), so nothing is dropped. The takeaway isn’t “every duck is a Holloman duck” — it’s that hotspots sit up and down every corridor, so the honest question is where your bird actually fed and watered. Installation roster and coordinates: TapWaterData Military PFAS Dataset (CC BY 4.0, 2026), parsing the DoD PFAS PA/SI list (Sept 30, 2025); EWG separately maps ~720 military AFFF sites among 9,700+ contaminated U.S. locations.

A note for the Pacific Flyway. Both of these studies are Eastern and Southwestern; no one has published an equivalent hunter-focused study for the ~60% of the flyway’s birds that winter in California’s Central Valley and Bay-Delta. Out West, mercury is the wildcard — a Gold Rush legacy that the region’s flooded rice fields and managed wetlands turn into methylmercury, driving the non-cancer advisory (and untouched by trimming). PFAS in Western waterfowl are essentially unstudied but turn up in Bay fish, so assume presence and watch for point sources exactly as above. See the flyway forecast below and your state’s OEHHA advisories.

The honest limitation: this is an Atlantic Flyway study. Here’s the directional inference for Pacific Flyway birds (California’s Central Valley and Bay-Delta) — clearly labeled reasoning, not measurement.

Atlantic data vs. a Pacific Flyway forecast

Directional inference by contaminant. Not measured — reasoned from regional pollution history.

Mercury is the Western wildcard (Gold-Rush legacy + methylmercury from rice fields and managed wetlands); it drives the non-cancer advisory, not cancer, and trimming won’t remove it. See your state’s OEHHA advisories.

The bottom line — or what I’ll be doing

  • Most ducks are a which-species-how-often question, and a good answer. Lean on what are likely clean species, skin-trim-cook, and eat within the cheat sheet.
  • A few ducks are a where-was-it-shot question, and the answer is no. Point-source PFAS — foam or sludge — produces birds thousands of times over the line, where species and preparation are irrelevant.
  • Tissue is the tell. Legacy contaminants hide in fat (trim them away); PFOS hides in lean meat and organs (you can’t). Skip the giblets from any suspect bird.
  • Know your water. The most protective thing you can do isn’t picking a species — it’s knowing whether the marsh you hunt sits downstream of a foam site, an outfall, or a sludge-fertilized field.

The hotspot layer — what’s modeled vs. measured

The background charts are the published Dayan et al. (2025) numbers, unchanged. The hotspot chart is a separate, clearly-labeled model. Dayan put only PFOA into their cancer math and said so — PFOS lacked a cancer slope factor “at the time of writing,” and they invited an update once one existed. EPA finalized the PFOS oral cancer slope factor (39.5 per mg/kg/day) and reference dose (1×10⁻⁷ mg/kg/day) in April 2024, so the hotspot uses those with the identical intake model (227 g meal, 80 kg, lifetime; CR = ADD × slope factor). Key assumption, stated plainly: Holloman’s headline PFOS values are liver, but hunters eat breast, so muscle is modeled at 0.2× the measured liver level (an assumption; 0.1–0.3× also computed). PFOS carries the cancer number (measured, dominant, now has a slope factor); PFOA is a labeled sensitivity only. Any risk above ~1 in 100 is past the slope factor’s valid linear range and should be read as “orders of magnitude past do-not-eat,” not a literal probability. Reproducible in hotspot_model.py.

Methods & honest caveats

All background figures are computed from the study’s own published per-bird dataset and risk outputs (Dayan et al. 2025). Cancer numbers are the conservative Total Cancer Risk, scaled linearly with meal frequency. “% higher” and multipliers use a ~40% baseline lifetime cancer chance (American Cancer Society). Baked-in assumptions: a ~½-lb (227 g) serving, 80 kg body weight, eaten at a fixed rate over a 70-year lifetime. Preparation scenarios apply literature-based reductions to fat-soluble contaminants only (35% cooked, 50% skinned/trimmed, 65% both). PFOS cancer term: the original study omitted PFOS from its cancer math for lack of a slope factor; we add it back using EPA’s April-2024 oral CSF (39.5 per mg/kg/day) applied to the authors’ own measured breast-muscle PFOS, per species (Cornell eCommons, doi:10.7298/0sss-m363) — exactly as their limitations section invited. Because PFOS binds protein and sits in lean muscle, it is prep-invariant: trimming and cooking do not reduce it, so the same PFOS term is added to every preparation (mercury is likewise held constant). The interactive cheat sheet lets you set the limit yourself — the non-cancer hazard index (the binding constraint at a 1-in-10,000 cancer target), a cancer-based limit, or the most protective of the two — at either a 1-in-10,000 or a stricter 1-in-100,000 risk, and for either ordinary Northeast birds or the Holloman hotspot. The study measured raw, skin-and-fat-on tissue and notes this overstates the fat-soluble risk for trimmed, cooked meat. “Typical” = mean; “cautious” = 95th percentile (teal n = 10, so treat its exact value as rough). A risk explainer, not medical advice.

Studies & sources

The four primary studies are 1, 2, 8 and 9. Everything on this page is computed from these public documents and datasets — see the public repo, the user guide, and the replication package.

  1. Dayan D, Hanley BJ, Stiller J, et al. (2025). Environmental contaminants assessment for frequently harvested migratory waterfowl in the Northeast Atlantic Flyway. Science of the Total Environment 963:178474. doi:10.1016/j.scitotenv.2025.178474 (open access). Per-bird dataset: Cornell eCommons, doi:10.7298/0sss-m363.
  2. New Mexico Environment Department (2025). Holloman Lake PFAS Ecology Report (Jan 8, 2025) — waterfowl PFOS/PFHxS tissue concentrations; statewide waterfowl composites; toxicity references (Newsted 2005).
  3. U.S. EPA (April 2024). Final Human Health Toxicity Assessment for PFOS and Related Salts (815-R-24-007) — oral cancer slope factor 39.5 (mg/kg/day)⁻¹; RfD 1×10⁻⁷ mg/kg/day.
  4. U.S. EPA (April 2024). Final Human Health Toxicity Assessment for PFOA and Related Salts (815-R-24-006) — CSF 2.93×10⁴ (mg/kg/day)⁻¹; RfD 3×10⁻⁸ mg/kg/day.
  5. Weyrauch et al. (2025), Food Protection Trends 45(3):155–162, and FDA Total Diet Study — PFAS in domestic meat: 95–99% of grocery beef/pork/chicken samples non-detect (USDA FSIS 2019–2023).
  6. U.S. EPA (2005). Guidelines for Carcinogen Risk Assessment — the 10⁻⁶ to 10⁻⁴ risk bands.
  7. Zabik ME, et al. (1995), J Agric Food Chem; NCCEH (2010); U.S. EPA (2000) — skin-off/cooking reductions for lipophilic contaminants.
  8. Eifert R-A, Gorski P, Magee M, Strom S (2025). PFAS in Mallard Breast Tissue and Surface Water in Green Bay, Wisconsin, USA. Environments 13(5):271. doi:10.3390/environments13050271 — direct breast-muscle PFOS; 67–>90% detection; ~480 ng/g max (lower bay). Discussed by co-author Sean Strom on Delta Waterfowl’s The Voice of the Duck Hunter, Ep. 104 (2026). Advisory: Wisconsin DNR/DHS (Sept 2025).
  9. LaSharr K, Carstensen M (2024). Waterfowl Exposure to Per- and Polyfluoroalkyl Substances (PFAS) in Minnesota, USA. Minnesota DNR Wildlife Research Summary — breast-muscle PFOS: Lake Elmo mallard median 948 ng/g (goose 31; clean control 0.4); cites Witt et al. (2024), Environ Res 249:118229, Holloman muscle mean 1,903 vs liver 9,154 ng/g.
  10. Associated Press (2022, 2025) — wild-game PFAS “do not eat” advisories (Michigan/Oscoda; Maine/Fairfield; Wisconsin/Marinette; New Hampshire); UNM coverage of Holloman.
  11. TapWaterData Editorial (2026), Military PFAS Dataset (CC BY 4.0), parsing the U.S. DoD PFAS PA/SI installation list (progress as of Sept 30, 2025) — 723 installations, 352 with public coordinates; the flyway map’s dots and per-state/flyway counts. State-to-flyway assignment: USFWS administrative flyways. EWG PFAS contamination map (2026) for the ~720 military AFFF-site and 9,700+ total-site figures.
  12. Hydes TJ, et al. (2019), BMC Public Health 19:316 (wine); IARC/WHO (2015) processed meat; Hites RA (2004), Science 303:226 / Huang X (2006), Environmental Research 101:263 (salmon) — the ladder’s food anchors.
  13. USGS — Mercury in birds of the San Francisco Bay-Delta & Central Valley; California OEHHA fish & game advisories.
  14. American Cancer Society — lifetime probability of developing invasive cancer (~40%).
  15. NYSDOH / CT DEEP / Cornell Wildlife Health Lab — waterfowl advisories: skin and remove fat; geese and wood ducks are lower-contaminant choices.