Hormone Guide · Dioxins, PCBs and endometriosis

Dioxins and PCBs: the trail that leads to endometriosis

In 1993 a research team found something nobody had been looking for. Ever since, people have asked whether environmental substances play a part in endometriosis. The answer is still not finished, but it is worth telling.

SJ
Shukri Jarmoukli · Physician · Area of focus: integrative medicine · ViveCura Berlin
The 1993 monkey study Seveso Aryl hydrocarbon receptor 34 verified sources

You are sitting in the car after the appointment, looking at a piece of paper. On it is a word that splits your life into a before and an after. And in your head runs a question that almost nobody says out loud, because it feels accusing: Why me?

I cannot answer that question for you. Nobody can. But I can tell you why, with hormonal complaints, I ask about things that at first glance have nothing to do with the lower abdomen. About the house you live in. About your parents' occupations. About the milk you drank as a child.

These questions come from a story that began in 1993. It is well documented, it is astonishing, and it has a second part that almost nobody tells. I will tell you both parts. Including the one that ruins the nice version.

My starting point

The question of whether dioxins set endometriosis in motion has been open for thirty years. Plausible, partly supported, not proven. That sentence is uncomfortable. It is still more honest than either of the two answers that circulate online.

What this article covers

  • The 1993 monkey study, told in full
  • What dioxins and PCBs actually are
  • The 2001 postscript that complicates everything
  • The aryl hydrocarbon receptor as a second switch
  • Seveso and what the human data can show
  • Two meta-analyses with two shades
  • Why exposure has fallen sharply since the 1980s
  • What follows in practice and where avoidance ends
clinical what I observe in my consultations, named as an observation human data from studies in people, observational or interventional animal data from animal models, not transferable to humans cell culture data from cells in the laboratory, the lowest tier
Please read first: what should not wait

This article is about background, not about emergencies. Some symptoms belong in medical hands promptly, regardless of what you read here.

  • bleeding after menopause
  • very heavy periods or periods that have suddenly changed
  • acute one-sided lower abdominal pain
  • lower abdominal pain together with fever
  • unintended weight loss
  • headaches or visual disturbances together with milk discharge from the breast
  • rapidly increasing signs of virilisation

And because endometriosis has warning signs of its own that do not have to hurt, here are the most important ones:

  • blood in the urine or in the stool that fits with the timing of your period
  • one-sided flank pain, or a urinary backup in the kidney seen on ultrasound
  • a change in bowel habit, up to cramping and vomiting
  • breathlessness or chest pain that returns cyclically

A urinary backup caused by endometriosis on the ureter can run for a long time without symptoms and still damage the kidney. That is exactly why it is listed here, even though it does not hurt. Please have these things assessed promptly. If breathlessness, chest pain or severe abdominal pain come on acutely, call the emergency number 112 and do not wait for a practice appointment.

And a second sentence that matters just as much: endometriosis is a medical diagnosis. The gynaecological assessment remains the foundation. Nothing in this text is a reason to postpone a recommended examination, an ongoing treatment or an indicated operation.

And if you have been trying to conceive without success for some time, that also belongs in a timely assessment. Time is a real factor in this topic, and nothing in this article is a reason to push a gynaecological or reproductive medicine assessment back.

A colony of monkeys and a finding nobody was looking for

Picture a research group that wanted to study something else entirely. Not the uterus. Not period pain. It was about the general toxicology of a substance that was then considered the most poisonous molecule ever made by humans.

A colony of rhesus monkeys received TCDD in their feed for four years. Two dose levels, 5 ppt and 25 ppt, plus a control group. Then the feeding ended. The animals went on living. Ten years later, researchers looked into the abdominal cavity with a laparoscopy.

What they saw there, nobody had expected.

animal model, primate The original observation

Who did it: A team around Rier, the first author then at the University of South Florida in Tampa, published the analysis of this colony in 1993.

What was observed: Endometriosis occurred more often and more severely in a dose-dependent way. Moderate to severe forms were found in 3 of 7 animals in the low dose group, which is 43 percent, and in 5 of 7 animals in the higher dose group, which is 71 percent. The 33 percent given for the control group refers to endometriosis of any severity, not to the moderate to severe forms. For comparison the paper drew on a group of 304 rhesus monkeys at the Harlow Primate Center without dioxin exposure, where the frequency of endometriosis of any severity was around 30 percent. The dose dependence of severity was statistically clear, with p less than 0.001.

What this means for you: This single paper set off the entire line of research into environmental factors in endometriosis. It shows that a substance with no similarity whatsoever to estrogen can influence how this disease develops. In monkeys. Not in humans. That difference is what this whole article is about.

Rier SE, Martin DC, Bowman RE, Dmowski WP, Becker JL. Fundam Appl Toxicol. 1993;21(4):433-441. PMID: 8253297 · DOI: 10.1006/faat.1993.1119 [In vivo, primate, n=7 per group]

Pause for a moment at those numbers. Seven animals per group. Seven. If a single animal had come out differently, the percentage would have shifted by 14 points. That is not an argument against the observation. It is an argument for keeping it in mind at the right size.

Two years later the same group followed up and looked at the immune status of the animals. The idea behind it: if a foreign substance lets tissue grow in the abdominal cavity, then perhaps not directly, but through the immune system, which would otherwise clear that tissue away. Cytokines as the link between foreign substance and tissue. That way of thinking is still the field's load-bearing hypothesis today.

animal model, primate The follow-up report on immune status

Who did it: The same working group published an analysis in 1995 with a focus on cytokines and immune competence.

What was observed: The frequencies stayed the same, 43 and 71 percent moderate to severe forms in the exposed groups, 33 percent endometriosis of any severity in the control group, 30 percent in the reference group of 304 animals. Here it is stated explicitly that moderate to severe forms were not found in the control group.

What this means for you: Suspicion turned early towards the inflammatory side. Not towards a hormone switch. That is unusual, and it is exactly why the paper was discussed so much.

Rier SE, Martin DC, Bowman RE, Becker JL. Environ Health Perspect. 1995;103 Suppl 7:151-156. PMID: 8593863 · DOI: 10.1289/ehp.95103s7151 [In vivo, primate]

There is a sentence from a later review by the same author that explains why the matter made waves. The serum concentrations of the exposed monkeys with endometriosis were similar to, or even lower than, blood levels in the general human population of that time.

It was not the height of the exposure that made the observation unsettling. It was that it was so low.

after Rier 2002, Ann N Y Acad Sci 955:201-212

With that, the question was no longer academic. It suddenly read: does this concern all of us?

Reframe

Many women read about this study and hear: environmental toxins cause endometriosis. That is not what it says. What it says is something else, and in a way something more interesting.

A substance that has nothing to do with estrogen can intervene in a disease considered an estrogen disease. That is the real discovery. It has widened the view of endometriosis, it has not replaced it.

And now you know why I ask about the exposure history. Not because I suspect a cause there. Because this line of research has shown that there is a second entrance into the system.

What dioxins and PCBs actually are

Before we go further, you need a picture of these substances. Otherwise everything that follows stays abstract.

Dioxins are not a product. Nobody wanted to make them. They arise as a side effect, whenever organic material is heated together with chlorine. When waste is burned. In metal processing. In the past as a contaminant in chlorine chemistry. Technically the term covers two families, the polychlorinated dibenzo-p-dioxins and the polychlorinated dibenzofurans, usually abbreviated in reports as PCDD and PCDF.

Polychlorinated biphenyls, PCBs for short, are the opposite. They were made deliberately, over decades, in large amounts. As insulating oil in transformers, as plasticisers, in sealants, lacquers and paints. They were non-flammable, chemically inert and cheap. Exactly the properties that made them attractive back then make them a problem today. In Germany their production has been banned since the 1980s.

A subset of the PCBs, the so-called dioxin-like PCBs, has a flat molecular shape and behaves in the body like a dioxin. The other subset, the non-dioxin-like PCBs, takes different routes. This distinction sounds like a detail. In the studies that follow, it decides the result.

Why these substances stay

Four properties that together make a problem

  1. Fat-soluble. They dissolve not in water but in fat. That is why they end up in fatty tissue and not in urine.
  2. Chemically stable. The body has no fast breakdown route for them. What goes in comes out only slowly.
  3. Accumulation along the food chain. A blade of grass carries little. A cow eats many blades of grass. A person eats many products from that cow over years. At every step the concentration rises.
  4. An inherited past. The amount in your body does not come from this week. It has built up over decades, part of it before you were born.
  5. Half-life without a fixed number. An analysis of more than 30 studies showed that the apparent half-life can be described through a linear relationship with age, taking body fat percentage, smoking and breastfeeding into account. So there is no single number that holds for everyone.

Source on the half-life: Milbrath MO, Wenger Y, Chang CW et al. Environ Health Perspect. 2009;117(3):417-425. PMID: 19337517 · DOI: 10.1289/ehp.11781 [Systematic Review]. The honest order of magnitude is years to decades, depending on the congener. Anyone who reads a single number of years is reading a simplification.

One more term you will meet in every report: TEQ, the toxic equivalent. There are hundreds of individual compounds in these families, and they differ in potency. So that they can be added up, each is given a factor relative to the strongest compound. That strongest compound is TCDD, written out as 2,3,7,8-tetrachlorodibenzo-p-dioxin, with the factor 1. A figure in picograms TEQ is therefore a conversion into a common currency.

And because I know that someone will want to compare figures from different reports: do not do it unchecked. There are TEQ factors from 1998 and from 2005, plus values from a bioassay called CALUX. Those are three different yardsticks. And picograms per kilogram per day is something other than picograms per kilogram per week.

A distinction that is often missing

Dioxins are not classic xenoestrogens

The term xenoestrogen describes foreign substances that dock onto the estrogen receptor and imitate something there. Bisphenol A belongs to that group. Zearalenone, a mould toxin, belongs to it very clearly, since it docks directly onto the estrogen receptor. More on that in our article on zearalenone as a mycoestrogen.

Dioxins do not belong to that group. They take a different entrance, more on that shortly. If you are interested in the classic endocrine disruptors of everyday life, meaning plastics, till receipts, cosmetics and dust, you will find them in xenoestrogens in everyday life. This article here is about a different class of substances with a different mechanism.

And now you know why these substances turn up in an article about hormones, even though chemically they have nothing to do with hormones.

The glitch in the story that has to be told

Here it gets uncomfortable. And here an honest text parts ways with one that only wants to convince.

Eight years after the first publication, the same working group looked more closely once more. This time not into the abdominal cavity but into the blood. What was actually in these animals, thirteen years after the feeding had ended?

animal model, primate The postscript from 2001

Who did it: Rier and colleagues, the first author by then at Dartmouth Medical School in Lebanon, New Hampshire, examined the serum of 9 exposed and 6 unexposed female animals for TCDD and 19 further dioxin-like compounds.

What was observed: The serum of the exposed animals contained not only TCDD. It also contained raised levels of 1,2,3,6,7,8-hexachlorodibenzofuran, of 3,3',4,4'-tetrachlorobiphenyl, PCB 77 for short, and of 3,3',4,4',5-pentachlorobiphenyl, PCB 126 for short. Animals with raised PCB 77, PCB 126 and raised total TEQ had a high frequency of endometriosis. And disease severity correlated with the serum concentration of PCB 77.

What this means for you: The colony's feed was apparently contaminated with PCBs as well. That made the experiment no longer a pure TCDD experiment. It remains a signal. But it is not clean proof that TCDD alone was responsible for the finding.

Rier SE, Turner WE, Martin DC, Morris R, Lucier GW, Clark GC. Toxicol Sci. 2001;59(1):147-159. PMID: 11134554 · DOI: 10.1093/toxsci/59.1.147 [In vivo, primate]

I find this part of the story more important than the first. Not because it devalues the original observation. Because it shows how science actually works. A sensational finding, a decade of thinking, then the realisation that the starting position was more complicated than assumed.

A third paper from the same year looked at immune cells. Thirteen years after the feeding ended, white blood cells from the exposed animals produced more TNF-alpha after stimulation, a signalling substance of inflammation, and their destructive activity against certain target cells was reduced. Other messenger substances were unchanged. Rier SE, Coe CL, Lemieux AM et al. Toxicol Sci. 2001;60(2):327-337. PMID: 11248145 · DOI: 10.1093/toxsci/60.2.327 [In vivo, primate]

Thirteen years. That is the point where I start to ponder in the consulting room. Not because I derive anything from it that the data cannot carry. But because it shakes the idea that an exposure is over when the exposure is over.

The dissenting voice that belongs here

Guo 2004: a critical reappraisal

Ten years after the first publication, Sun-Wei Guo, then at the Medical College of Wisconsin in Milwaukee, presented a critical review of all available primate and human data. He explicitly calls the original observation a chance finding that sent a shock wave through the research community.

His conclusion is clear. The primate data, he writes, remain ambiguous, and the human data are sparse and contradictory. There is some indication that dioxin exposure could favour the short-term survival of transplanted endometrial tissue in non-human primates. For the development of spontaneous endometriosis he saw, at that point, no solid, credible data supporting the hypothesis.

This assessment dates from 2004. Since then meta-analyses have been added that show a moderate signal for PCBs. But the core of the criticism has not been refuted, and that is why it stands here in the text and not in a footnote.

Guo SW. Gynecol Obstet Invest. 2004;57(3):157-173. PMID: 14739528 · DOI: 10.1159/000076374 [Mechanism Review, critical reappraisal]

There is a second obvious explanation that has been tested and not confirmed. It goes: some people break these substances down less well, and that is why they fall ill. The same author systematically reviewed ten studies in 2006 on gene variants of foreign substance detoxification, among them CYP1A1, CYP2E1, EPHX1, AHR, ARNT, AHRR, NAT1 and NAT2. Almost none of the variants examined showed a link to endometriosis. For one variant of the CYP1A1 gene a roughly 40 percent increased risk was found, without consistent confirmation in other work.

Reframe

Online there is a story going round that some women get endometriosis because their detoxification is genetically weak. The idea is plausible, it has been studied, and it has not been confirmed.

If someone sells you a genetic test that explains your endometriosis through detoxification, you can hold this paper up against it. Anyone who takes the link between environment and hormones seriously also has to name the places where the simple explanation does not hold.

And now you know why I am careful in this field. The nice story has a postscript. Telling it without the postscript means telling it wrong.

The aryl hydrocarbon receptor, a second switch

If you have read this far, you have probably already asked yourself: how is that even supposed to work? A substance that has nothing to do with estrogen intervenes in a hormone-dependent disease. Where is the lever?

It is called the aryl hydrocarbon receptor, in the literature usually AhR. Picture it as the smoke detector of the cell. It hangs inside the cell and waits. If a foreign molecule with the right flat shape comes past, it docks on. The smoke detector travels into the cell nucleus and switches genes on there, above all genes for enzymes meant to convert foreign substances.

At first this is a sensible arrangement. The body recognises something foreign and prepares its breakdown. The problem arises when the smoke detector no longer switches off, because the substance stays. Then a programme designed for short assignments runs permanently.

cell culture mouse model The cleanest mechanistic work in the field

Who did it: A group at the Key Lab of Urban Environment and Health of the Chinese Academy of Sciences in Xiamen compared two PCBs with each other: the dioxin-like CB126 and the non-dioxin-like CB153, in primary cultured endometrial cells and in a mouse model of endometriosis.

What was observed: CB126 raised the formation of estradiol in a dose-dependent way, CB153 did not. Among the genes of estrogen metabolism, 17-beta-hydroxysteroid dehydrogenase 7 rose above all, and the methylation of its promoter fell. Increased activity of this gene was also found in the endometrium of women with endometriosis. In the mouse model, estradiol and inflammatory markers rose in the peritoneal fluid and the lesions grew more strongly. A blocker of the aryl hydrocarbon receptor abolished these effects.

What this means for you: It is not the substance class PCB that decides, but the molecular shape. And the route runs through the aryl hydrocarbon receptor. This is cell culture and mouse. For humans nothing is proven by it.

Huang Q, Chen Y, Chen Q, Zhang H, Lin Y, Zhu M, Dong S. Arch Toxicol. 2017;91(4):1915-1924. PMID: 27663891 · DOI: 10.1007/s00204-016-1854-0 [In vitro, In vivo, mouse]

So what happens when the smoke detector is permanently on? A second piece of work on human endometrial cells from Winnipeg in Canada examined exactly that. Dioxin-like compounds activated the aryl hydrocarbon receptor in a time-, concentration- and substance-dependent way. What was remarkable was what did not happen: the estrogenic processes in these cells were not disturbed by it. Independently of binding to the receptor, the migratory capacity of the cells rose.

That is the actual evidence for the sentence that dioxins are not classic xenoestrogens. They do not need the estrogen receptor.

Mechanistically plausible, human data thin

What the route looks like in theory

  1. Docking. A flat, chlorine-rich molecule binds to the aryl hydrocarbon receptor inside the cell.
  2. Gene programme. The receptor travels into the cell nucleus and switches genes on, among them genes for enzymes of foreign substance conversion such as CYP1A1.
  3. Inflammation. In cell culture with hexachlorobenzene, a dioxin-like substance and a weak ligand of the same receptor, COX-2 and the release of prostaglandin E2 rose, along with the activity of the matrix metalloproteinases MMP-2 and MMP-9, the tools with which cells clear paths through tissue.
  4. Local estrogen production. In the rat model, likewise with hexachlorobenzene, aromatase rose in the lesions, as did estrogen receptor alpha, while the progesterone receptor was lower.
  5. Tissue grows. In both animal models, the mouse model with PCB 126 and the rat model with hexachlorobenzene, the size and blood supply of the lesions increased.

Evidence: Willing C, Peich M, Danescu A et al. Mol Hum Reprod. 2011;17(2):115-126. PMID: 20876610 · DOI: 10.1093/molehr/gaq081 [In vitro]. The two papers that follow studied hexachlorobenzene, not dioxin or PCBs. Chiappini F, Baston JI, Vaccarezza A et al. Biochem Pharmacol. 2016;109:91-104. PMID: 27038655 · DOI: 10.1016/j.bcp.2016.03.024 [In vitro]. Chiappini F, Sanchez M, Miret N et al. Food Chem Toxicol. 2019;123:151-161. PMID: 30393115 · DOI: 10.1016/j.fct.2018.10.056 [In vivo, rat]. Important: not one of these markers has been measured in humans as a response to a changed exposure.

Aromatase and the progesterone receptor are exactly the settings that are already altered in endometriosis. That makes the observation interesting. It does not make it proof. The rat study used partly very high doses, it dealt with hexachlorobenzene rather than dioxin itself, and rats are not women.

One paper that combined exposure modelling, meta-analysis and gene analysis found five genes influenced jointly by PCBs, bisphenols and phthalates: CYP19A1, EGFR, ESR2, FOS and IGF1. CYP19A1 is the gene for aromatase, the enzyme that produces estrogen in the tissue itself. That is the most direct molecular bridge between an environmental substance and local estrogen production in a lesion. It is bioinformatic, not clinical. Roy D, Morgan M, Yoo C et al. Int J Mol Sci. 2015;16(10):25285-25322. PMID: 26512648 · DOI: 10.3390/ijms161025285 [Bioinformatics, meta-analysis]

Reframe

Many women know the idea that endometriosis is a disease of too much estrogen. That falls short. A large part of the estrogen in a lesion is produced there on site, independently of the ovary.

The interesting lever is therefore not the blood level but the regulation in the tissue itself. That is exactly where the mechanisms described here act. And that is exactly why inflammation is at the centre and not the hormone value. What can sensibly be measured and what cannot is covered in hormone testing in women.

And now you know why I do not say that dioxins work like estrogens. They take a different entrance, and that entrance leads through inflammation.

What the human data can show and what it cannot

Now comes the part that really counts. Everything so far was monkeys, mice, rats and cells. Humans are none of those.

The question is: is there a population in which this can be tested? You cannot give women dioxin. So it takes a sad coincidence. And there was one.

On 10 July 1976 a reactor exploded at a chemical plant near Seveso in northern Italy. A cloud containing large amounts of TCDD settled over the surroundings. Years later the Seveso Women's Health Study grew out of this disaster, the best documented cohort with high TCDD exposure that exists.

Before the study proper, a question arose that somebody had to calculate: were the women in Seveso exposed at a level comparable to the monkeys of 1993 at all? A toxicokinetic analysis from Berkeley concluded that the cumulative exposure of the most affected residents was in every case above the exposure of both monkey groups. That made Seveso the decisive test cohort.

cohort study in humans The most honest number in the whole field

Who did it: A group around Brenda Eskenazi published in 2002 the analysis of 601 women from the Seveso area who were at most 30 years old in 1976 and for whom stored serum from the time right after the accident was available.

What was observed: 19 women had endometriosis, 277 were classified as not affected. Compared with TCDD levels up to 20 ppt, the relative risk ratio was 1.2 for values between 20.1 and 100 ppt, with a 90 percent confidence interval from 0.3 to 4.5. For values above 100 ppt it was 2.1, with a 90 percent confidence interval from 0.5 to 8.0. The trend tests were not significant. The authors describe a doubled, non-significant risk without a clear dose-response relationship and point out that unavoidable misclassification may have led to an underestimate of the true risk.

What this means for you: The most heavily exposed known population delivers a trend and no proof. A confidence interval from 0.5 to 8.0 is compatible with almost any result. Nineteen cases are simply too few.

Eskenazi B, Mocarelli P, Warner M et al. Environ Health Perspect. 2002;110(7):629-634. PMID: 12117638 · DOI: 10.1289/ehp.02110629 [Cohort, n=601]

So that nobody draws the wrong conclusion: this cohort has indeed delivered clear results, just in a different place. In follow-up to 2008, 66 of 833 women had a cancer diagnosis. Per tenfold rise in serum TCDD, the adjusted hazard ratio for all cancers combined was 1.80, with a 95 percent confidence interval from 1.29 to 2.52. For breast cancer it was 1.44 and not significant.

That matters for context. TCDD is toxicologically not harmless. The open question is only whether endometriosis of all things is its target organ.

So that this figure does not land wrongly, one clear sentence about it: it stands here purely to place the substance group, and not to worry you. It comes from the cohort with the highest TCDD exposure ever documented and cannot be transferred to everyday exposure today. Nothing follows from it, neither an examination I would offer you here nor a need for you to act. Warner M, Mocarelli P, Samuels S, Needham L, Brambilla P, Eskenazi B. Environ Health Perspect. 2011;119(12):1700-1705. PMID: 21810551 · DOI: 10.1289/ehp.1103720 [Cohort, n=833]

Three investigations in humans, three answers. All three are carefully done. They measure different things.
InvestigationWhat was measuredResult
Seveso, Italy
601 women, 19 cases
serum TCDD from the year of the accidentrisk ratio 2.1 above 100 ppt, 90 percent interval 0.5 to 8.0, no trend
Rome, Italy
80 cases, 78 controls
individual PCB congeners, DDE, hexachlorobenzene, plus total TEQclearly raised odds ratios for several PCBs, but no signal for total TEQ
Washington, USA
251 cases, 538 controls
20 non-dioxin-like PCB congeners in serumno consistent pattern, summed value odds ratio 1.3 with 95 percent interval 0.8 to 2.2

The Roman work by Maria Grazia Porpora and colleagues at Sapienza University is the strongest positive human study there is. For the dioxin-like PCB 118 the odds ratio was 3.79 with a 95 percent confidence interval from 1.61 to 8.91, for PCB 153 it was 4.88 with an interval from 2.01 to 11.0, and for the sum of dioxin-like and non-dioxin-like PCBs it was 5.63 with an interval from 2.25 to 14.10.

And in the same data set, of all things the total TEQ from dioxins, furans and dioxin-like PCBs was not linked with endometriosis. So precisely the measure that expresses the actual dioxin burden. This nuance is missing online across the board, and it belongs here.

The counter-check comes from the US state of Washington. Britton Trabert and colleagues examined 20 PCB congeners in 251 surgically confirmed cases and 538 age-matched controls. Individual congeners even fell below the null value, for example PCB 196 with an odds ratio of 0.4. The authors' conclusion: non-coplanar PCBs do not contribute meaningfully to endometriosis risk in the exposure range observed there.

The most important methodological caveat

Why exposure measured backwards is a problem

In almost all case-control studies, blood is drawn after the diagnosis. For substances that gather in fatty tissue, that is delicate. Weight loss releases stored substances and raises the blood value. Weight gain dilutes it. Periods of breastfeeding lower it. And a chronic illness changes fat metabolism.

It is therefore possible that part of the association found does not mean that the exposure led to the illness, but that the illness and its course influenced the measurements. So far no study in the field can rule this objection out.

A smaller Roman paper closed the loop back to immune status. In women with endometriosis, the activity of natural killer cells was reduced, as were IL-1-beta and IL-12. Total PCB concentration was 330 versus 160 nanograms per gram of fat in the controls, DDE 770 versus 310. In the test tube, PCBs and DDE lowered the activity of these cells. Quaranta MG, Porpora MG, Mattioli B et al. Life Sci. 2006;79(5):491-498. PMID: 16499933 · DOI: 10.1016/j.lfs.2006.01.026 [Case-control, small sample, plus in vitro]

That is a small study, it is an association, and the caveat from a moment ago applies here too. It is interesting all the same, because it carries the same line of thought as the monkey colony of 1995. Immune status as the link. If you want to know how inflammation and metabolism interlock in women, you will find it in insulin resistance and female hormones.

And now you know why I do not give a short answer to the question about proof. There is none.

Two meta-analyses, two shades

When individual studies contradict each other, you add them up. That is the point of a meta-analysis. It is no magic wand, but it sorts things.

On environmental substances and endometriosis there are two larger pieces of work of this kind. They point in similar directions and arrive at differently strong numbers. Why, I will tell you in a moment.

meta-analysis 30 epidemiological studies

Who did it: A group at the Reproductive Medicine Center of Zhongnan Hospital of Wuhan University searched PubMed, EMBASE and Web of Science up to January 2018 and included 20 publications with 30 individual studies.

What was observed: Across all exposures together the odds ratio was 1.41 with a 95 percent confidence interval from 1.23 to 1.60. For PCBs it was 1.58 with an interval from 1.18 to 2.12, for organochlorine pesticides 1.40 with an interval from 1.02 to 1.92, and for phthalate esters 1.27 with an interval from 1.00 to 1.60. These last two values are borderline, and for the phthalate esters the lower bound sits exactly on 1.00. Bisphenol A showed no significant link.

What this means for you: A reproducible, moderate signal for PCBs. And a surprise: bisphenol A of all things, the substance most written about online, does not make the cut here.

Wen X, Xiong Y, Qu X, Jin L, Zhou C, Zhang M, Zhang Y. Gynecol Endocrinol. 2019;35(8):645-650. PMID: 30907174 · DOI: 10.1080/09513590.2019.1590546 [Meta-analysis, k=30]
systematic review and meta-analysis 14 studies, PCBs only

Who did it: A group at Babol University of Medical Sciences in Iran searched five databases for work from 2000 to the end of 2020, without language or country restriction, and calculated with a random effects model.

What was observed: The pooled odds ratio for PCBs was 1.96 with a 95 percent confidence interval from 1.31 to 2.93, at moderate heterogeneity with I squared equal to 63 percent. In the European subgroup it was 3.66, in studies with laparoscopically confirmed cases 2.32, in studies with surgically checked controls 1.39 and in studies with a matched-pairs design 1.51, where heterogeneity fell to 30.4 percent.

What this means for you: That is the decisive observation of this whole section. The cleaner the study design, the smaller the effect. The signal is probably real and probably smaller than the most eye-catching numbers suggest.

Shirafkan H, Abolghasemi M, Esmaeilzadeh S, Golsorkhtabaramiri M, Mirabi P. J Gynecol Obstet Hum Reprod. 2023;52(5):102574. PMID: 36918125 · DOI: 10.1016/j.jogoh.2023.102574 [Meta-analysis, k=14]

A word on heterogeneity, because otherwise the term says nothing. I squared describes how strongly the individual results differ from one another, beyond chance. 63 percent means: the studies are not telling the same story. In the subgroup with the strictest design this value fell to 30 percent, and there the effect was 1.51 instead of 1.96.

How to read numbers like these

Three questions that turn any headline into context

How certain was the diagnosis?
Was the endometriosis seen during a laparoscopy or derived from a questionnaire? And how was it checked that the control group really does not have it? Both shift the result considerably.
What exactly was measured?
Individual congeners, a summed value or the total TEQ. These three measures are not interchangeable, and a study can show a signal for one of them and not for another.
When was it measured?
Before the illness or after it. Only the Seveso cohort has serum from the time before diagnosis. That is why its weak result carries so much weight.

These three questions explain most of the contradictions in the field. Not sloppiness, but different study designs.

There are two further review papers that round off the picture. A systematic screening of 27 papers on endocrine disruptors, microRNA and endometriosis placed dioxins, organochlorine pesticides and PCBs as the better documented group, while bisphenol A and phthalates delivered contradictory results. The signalling pathways involved were NF-kappa-B, MAPK and Wnt/beta-catenin. This work does not add up, it sorts, and is therefore weaker than the two meta-analyses. Chandrakanth A, Firdous S, Vasantharekha R et al. Reprod Sci. 2024;31(4):932-941. PMID: 38036864 · DOI: 10.1007/s43032-023-01412-8 [Systematic review, k=27]

The highest available tier is an umbrella review from 2024 that summarised 52 systematic reviews with a total of 759 meta-analyses on plastic-associated chemicals. There, PCBs in the general population are linked among other things with endometriosis, and also with type 2 diabetes, cardiovascular disease and breast cancer. The postscript belongs with it: 78 percent of the included meta-analyses came from reviews of merely moderate methodological quality. Symeonides C, Aromataris E, Mulders Y et al. Ann Glob Health. 2024;90(1):52. PMID: 39183960 · DOI: 10.5334/aogh.4459 [Umbrella review]

The sentence that matters

There is a link between PCBs and endometriosis, and it has been found more than once. It is moderate, method-dependent and not proven as a cause. And it certainly does not explain endometriosis on its own.

Reframe

An odds ratio of 1.5 sounds like a lot. But it does not mean that half of all cases come from PCBs. It describes a statistical difference between groups, not your personal fate.

And more importantly: it does not follow from this that every hormonal disturbance has an environmental cause. Environment is one level among several. Genetics, the immune system, inflammatory status, metabolism and life history all play a part. Why I look at endometriosis as a networked process is set out in endometriosis: an integrative view.

And now you know why two serious papers on the same topic deliver different numbers. They selected with different degrees of strictness.

The good news that is rarely told

If you have read this far, you may be feeling uneasy. So now comes the part that environmental articles like to leave out, because it takes away the drama.

Exposure has fallen sharply. Not a little. Sharply. And that is not a claim but documented across several independent measurement series.

biomonitoring, time series Forty years of breast milk

Who did it: A group at Stockholm University analysed breast milk samples from Stockholm from 1972 to 2011 using high-resolution mass spectrometry and evaluated the trends statistically.

What was observed: The sum of PCDDs, the sum of PCDFs, the sum of dioxin-like PCBs and the total TEQ fell statistically significantly by 5.8 to 6.8 percent per year between 1972 and 2011. In the last ten years of that period the annual decline for the sum of PCDDs, the sum of dioxin-like PCBs and the total TEQ was 9.2 to 11 percent, and for the sum of PCDFs 5.4 percent.

What this means for you: Exposure has not only fallen. The decline had even accelerated most recently. Regulation can move something, and here it can be checked with arithmetic.

Fång J, Nyberg E, Bignert A, Bergman Å. Environ Int. 2013;60:224-231. PMID: 24080458 · DOI: 10.1016/j.envint.2013.08.019 [Environmental biomonitoring, time series 1972 to 2011]
5.8 to 6.8 %annual decline in Swedish breast milk, 1972 to 2011
factor 3.2decline in dietary intake of PCDDs, PCDFs and dioxin-like PCBs in France
around 94 %less dioxin in Bavarian bulk dairy milk since 1989, official figure

The French figure comes from the second national Total Diet Study. 583 ready-to-eat food samples were analysed and combined with national consumption data. Compared with the previous assessment, exposure fell by a factor of 3.2 for PCDDs, PCDFs and dioxin-like PCBs together. Fewer than 4 percent of the population exceeded the health-based guidance value.

From Ireland comes a second independent confirmation. There the mean intake of total TEQ was 0.3 picograms per kilogram of body weight per day, and 1 picogram at the 95th percentile. All values were below the health-based guidance values that applied at the time. Tlustos C, Anderson W, Flynn A, Pratt I. Food Addit Contam Part A. 2014;31(6):1100-1113. PMID: 24645880 · DOI: 10.1080/19440049.2014.905713 [Exposure estimate]

The German figure comes from the Bavarian State Office for Health and Food Safety, which has examined more than 1,000 samples of bulk dairy milk since 1989. The average dioxin content has fallen by around 94 percent. The second part of this statement matters: for about ten years, exposure has been stagnating at this low level. The easy road has been travelled.

Regulatory assessment

Why the EFSA tightened the limit anyway

In 2018 the European Food Safety Authority lowered the tolerable weekly intake to 2 picograms TEQ per kilogram of body weight per week, expressed in the WHO factors of 2005. That is around seven times lower than the value that had applied before.

The critical endpoint of this calculation was not endometriosis. It was sperm concentration, derived from a cohort of boys and young men. [Regulatory risk assessment] The core statement of the assessment is that exposure in early life phases can impair male reproductive capacity.

I find that revealing. The authority takes these substances very seriously. It simply does so at a different place in the body than endometriosis research does. Knowing both at the same time is the most honest position.

EFSA CONTAM Panel. EFSA Journal. 2018;16(11):5333. DOI: 10.2903/j.efsa.2018.5333 [Regulatory risk assessment]

The catch in the reassuring numbers

The calculation was made against an older benchmark

The Irish and the French assessments were made before 2018. They were calculated against the guidance value that applied then, 14 picograms per kilogram of body weight per week. If you scale the Irish average intake of 0.3 picograms per day up to a week, you arrive at around 2.1 picograms, which is just above the value of 2 picograms that applies today. The 95th percentile of 1 picogram per day corresponds to around 7 picograms per week.

The Flemish survey belongs here in full as well. In it, 59.8 percent of adolescents, 53.7 percent of mothers and 36.2 percent of adults exceeded the then guidance value of 14 picograms per week, and adolescents were highest per kilogram of body weight. Because these values were collected with the CALUX bioassay, they are not directly comparable with mass spectrometry figures, and because they date from 2007 they cannot be transferred one to one to today. Bilau M, Matthys C, Baeyens W et al. Chemosphere. 2007;70(4):584-592. PMID: 17720214 · DOI: 10.1016/j.chemosphere.2007.07.008 [Exposure estimate, dietary survey, n=4,408]

The decline is real and it is large. Measured against today's benchmark it is nevertheless not yet at its goal. Both belong in the same paragraph, otherwise a piece of good news turns into a number that has been made to look good.

Where does exposure come from today in concrete terms? The best breakdown comes from the same Flemish survey with several thousand participants. Fish and seafood contributed 25 to 43 percent of total intake, added fats 22 to 25 percent, dairy products 17 to 20 percent.

Two qualifications on that, because I do not want to make numbers prettier than they are. The data come from 2007 and were collected with a bioassay that gives different numbers than mass spectrometry. They show the distribution of sources, not today's exposure level. The distribution itself has remained plausible, because the physics does not change: these substances sit in fat.

Reframe

When I talk about environmental substances in the consulting room, I often hear the sentence: there is nothing you can do about it anyway. These numbers say something else.

Between 1972 and today, a great deal has moved in Europe at exactly this point, without any single person having to do anything for it. That is no reason to be careless. It is a reason to look at the matter with a calm pulse.

And now you know why I do not leave this section out, even though it takes away the drama. A text about the environment that only points downwards is not a good text.

What follows in practice, and where avoidance runs into limits

Let us come to the question you probably had from the start. What do I do with this now?

The honest answer begins with a limitation. Most of what is in your body got there over decades. Part of it before you were born. What you do differently from tomorrow changes that stock only slowly.

That is no reason to do nothing. It is a reason to keep expectations of your own action realistic.

Three levers that follow from the data

  • Fat of animal origin is the carrier. These substances sit in fat, not in muscle and not in vegetables. Anyone who scales back the share of very fatty animal products in everyday life can reduce the input. That is arithmetic, not a promise.
  • Origin beats amount. Where an animal lived and what it ate decides its content. That is why asking about the origin of a food makes more sense than asking how many grams of it are allowed.
  • What you no longer bring in, the body no longer has to get rid of. For substances with a residence time of years, avoidance is the approach with the best justification behind it. For procedures meant to pull these substances out of the body there are no robust data in endometriosis.

When you are trying to conceive

For many women, endometriosis and trying to conceive belong together, and this section matters to me in particular. Here a factor plays a part that no environmental measure influences: time.

If you have been trying to conceive without success for some time, that belongs in a gynaecological and, depending on the situation, reproductive medicine assessment, and promptly. Nothing in this article is a reason to wait with that until you have sorted out your surroundings. Both run side by side, not one after the other.

And I want to be very clear at this point: I cannot tell you that anything will change for your fertility if you change your everyday life, and I will not hold it out as a prospect either. There is no intervention study on this question. What I can say is more modest. The questions about housing, occupation and exposure history cost little time, they do not stand in the way of an assessment, and sometimes they bring something to light that can be addressed. They do not replace the assessment.

And what about an ongoing treatment?

A large part of endometriosis treatment runs through prescription medicines. These include combined hormonal contraceptives, colloquially the pill, progestin-only preparations, in Germany above all the substance dienogest for endometriosis, in certain situations GnRH analogues, along with pain treatment and, where indicated, an operation. All of these are prescription medicines. They require a medical examination, an indication and a prescription.

Each of them has a risk side of its own, and that belongs next to the name. Under combined hormonal contraceptives the risk of thrombosis and embolism can be raised, more clearly with smoking, with higher age, with obesity and with certain clotting disorders. Under progestins, breakthrough bleeding, mood changes and a drop in libido can occur. Under GnRH analogues bone density can decrease, which is why they are usually given for a limited period and often together with what is called add-back therapy.

And one point that is rarely mentioned: in Germany the combined pill is mostly prescribed for endometriosis outside its licence, that is, off label. This means separate counselling, a particular duty of medical justification and, as a rule, no reimbursement by statutory health insurance. Dienogest, by contrast, is licensed for this indication.

Which of these might be right for you, which contraindications apply in your case and what dose is appropriate is settled by the doctor treating you. That is why doses deliberately do not appear in this text.

So one clear sentence on that: nothing in this article implies that you should stop, lower the dose of or pause any of these medicines. Every adjustment of a medication belongs in a medical conversation and needs medical supervision, even when it seems small to you. If you are unhappy with what you are taking, that is a good reason for a conversation and not a reason to go it alone. The same applies to thyroid hormones, to metformin and to hormone replacement therapy, if you are receiving any of them alongside.

And one more clarification, because this topic is often presented crookedly online: bioidentical hormones are prescription medicines too. They are not gentle self-help, they need an indication, a medical prescription and follow-up. Doses therefore do not belong in an article, but in a treatment.

Fish: why I draw a distinction here

Fish appears in the exposure data as the largest single source of dioxin-like compounds, with 25 to 43 percent of total intake in the Flemish survey. That is why it appears in this section.

With large predatory fish a second point comes on top, one that has nothing to do with dioxins: mercury content. It concerns above all long-lived predators at the end of the food chain, that is shark, swordfish, marlin, pike and large tuna. From those I advise against. Small, short-lived fish such as sardine, anchovy or herring sit lower down the chain and carry considerably less mercury. Why I look so closely at metals is set out in heavy metals in pregnancy and childhood.

And now the counter-argument that belongs here, because my reticence is not the official recommendation. The German Nutrition Society still advises regular sea fish, in the order of about one portion per week. The German Federal Institute for Risk Assessment recommends avoiding large predatory fish in pregnancy, not avoiding fish altogether. The reason for that carries weight. Sea fish is one of the most important carriers of iodine in the German diet, and iodine matters in pregnancy for the development of the child's brain. On top of that come the long-chain omega-3 fatty acids.

So if you leave fish out, iodine and these fatty acids should be covered another way. Please do not decide that on the basis of this article, and certainly not if you are pregnant or would like to become pregnant. That question belongs with your gynaecologist or your midwife.

Breastfeeding: please read this paragraph to the end

Fat-soluble pollutants pass to the child through breast milk. That is not disputed, and for the mother, breastfeeding is indeed a route of excretion. That is exactly why breastfeeding appears in the half-life formula at all.

And the National Breastfeeding Committee at the German Federal Institute for Risk Assessment, together with the gynaecological and paediatric professional societies, still advises breastfeeding, explicitly in view of this pollutant burden too. Please keep this sentence, if you forget the rest.

A review from the predecessor institute of today's German Federal Institute for Risk Assessment in Berlin frames it like this: the restrictions on production, use and release were successful, visible in a downward trend in breast milk and blood lipids. Transfer before birth is considered more significant for the child's physical development and cognitive function than exposure after birth through breast milk. And the breastfeeding period makes up only about 0.6 percent of the expected lifespan. Przyrembel H, Heinrich-Hirsch B, Vieth B. Adv Exp Med Biol. 2000;478:307-325. PMID: 11065082 · DOI: 10.1007/0-306-46830-1_27 [Review]

For the sake of honesty, the sentence the same paper writes in the same breath belongs here too: intake through breast milk in industrialised countries is ten to a hundred times higher than the tolerable daily intake the WHO derived in 1998. The paper dates from 2000, and exposure has fallen considerably since. The weighing-up still comes out in favour of breastfeeding, because transfer before birth is considered more significant and because the breastfeeding period makes up only this very small part of the lifespan. The authors close explicitly by saying that carefully conducted long-term cohorts have yet to deliver the final answer.

This weighing-up does not belong in an article, and certainly not in a night with a phone in your hand. It belongs in a conversation with your midwife, your paediatrician or your gynaecologist.

Why I usually do not order dioxin blood tests

Technically they are possible. In everyday practice they are rarely useful. The analysis needs high-resolution mass spectrometry and a lot of sample material, it is laborious and hardly available outside specialised laboratories.

The more important reason is a different one. A measurement is useful when it changes a decision. Here it changes none. There is no treatment whose use depends on this value, and no study showing that lowering the value influences the course of endometriosis. What remains is a number that unsettles and opens nothing.

For other groups of substances it looks different, and the distinction matters. What can sensibly be measured with heavy metals and what cannot is covered in measuring heavy metals in blood or urine.

The paragraph that matters most to me

In my consultations I regularly see what an article like this one can do when it lands wrongly. A piece of information becomes a list. The list becomes a ban. The ban becomes fear of eating. And at some point everyday life is a minefield in which every meal is a test.

That is no gain in health. It is a loss of life, and it can lead into an eating disorder. If you notice that thoughts about purity, origin and contamination are starting to govern your day, please get support. In Germany the eating disorder helpline of the Federal Centre for Health Education can be reached on 0221 892031. The Telefonseelsorge is available around the clock and free of charge on 0800 111 0 111 and on 0800 111 0 222. If it is acute and you are thinking about self-harm or suicide, please call the emergency number 112. We also have a separate text on this topic: understanding eating disorders: body and mind.

And one more thing: no sentence in this article means that you are to blame for your illness. Endometriosis does not arise from eating wrongly. The question about the environment is a question about circumstances you have lived in, not about decisions you got wrong.

What the guidelines say, and why so little

I am occasionally asked in my consultations why this is rarely mentioned at the gynaecologist's practice. The answer is less spectacular than many expect, and it is not a reproach to anyone.

The current German-language S2k guideline on endometriosis states on lifestyle factors that there are still no clear or robust findings, and that this applies equally to body weight, smoking, caffeine, alcohol, diet and physical activity. It then adds that there are isolated indications of environmental influences that may carry risk, and that chemicals such as polychlorinated biphenyls, bisphenol A and phthalates have been linked with gene changes and inflammatory processes. I did not find the word dioxin in the risk factor section of the long version. [Guideline] S2k guideline endometriosis, AWMF registry number 015/045, long version dated April 2025. The English-language journal version of the same guideline is available under PMID: 41684533.

The European ESHRE guideline gives no recommendation at all on environmental factors. Its only statement on prevention is, in essence, that women can be advised to lead a healthy lifestyle, although there is no direct evidence of a preventive benefit. The strength of that recommendation is weak. [Guideline] ESHRE guideline endometriosis 2022. PMID: 35350465

How I place this

It is not interest that is missing. It is the intervention study.

Guidelines recommend actions that have been tested. For the question of whether lower exposure to dioxins or PCBs changes the course or the occurrence of endometriosis, there is not a single intervention study. For substances with a residence time of years, such a study is barely feasible. You would have to follow people for decades and deliberately alter their exposure.

That is why guidelines say little. Not because someone is overlooking something, but because the same standards are applied consistently that also apply to alcohol, coffee and exercise. This restraint is understandable, and I share its standard.

What I do in addition is something else and replaces none of that. I ask about housing, occupation, mould, exposure history and inflammatory status. This is my clinical observation and not a study result: sometimes something comes out of it that can be addressed, and often it does not. Whether that changes the course of an endometriosis has not been studied. The gynaecological assessment remains the foundation. The environmental perspective comes on top, not in its place. And the professional society for endocrinology itself urges caution in its large statement on endocrine disruptors when it comes to inferring causes in humans from animal data.

Reframe at the end

This line of research did not teach me that dioxins cause endometriosis. It taught me something else, which carries more weight in everyday practice.

A substance can intervene in hormone and inflammation biology through a second receptor route, without resembling a hormone. If that holds for dioxins, it probably holds for other substances we know less about. That is why I ask about the surroundings a person lives in. Not because I suspect the cause there, but because there lies a level nobody else looks at.

And the obligatory sentence, which I have written once already and which is worth standing twice: it does not follow from this that every hormonal disturbance has an environmental cause. For many symptom patterns the answer lies elsewhere, for example with stress and the adrenal axis, as described in cortisol, stress and female hormones.

And now you know why, on the subject of environment and hormones, I neither reassure nor alarm. Either would be easier. Either would be wrong.

Frequently asked questions

What are dioxins, and where do they come from?

Dioxins are not a product anyone set out to make. They form as a by-product wherever organic material is heated together with chlorine: in combustion processes, in metal processing, and in the past in chlorine chemistry. Technically the term covers two groups of substances, the polychlorinated dibenzo-p-dioxins and the polychlorinated dibenzofurans. They dissolve in fat and are very stable, which is why they accumulate along the food chain. Today they enter the body mainly through foods of animal origin.

What is the difference between dioxins, furans and PCBs?

Dioxins and furans are by-products. Polychlorinated biphenyls, by contrast, were made deliberately, for decades, as insulating oil in transformers, as plasticisers, in sealants and paints. In Germany their production has been banned since the 1980s. Chemically the three groups are related, and a subset of the PCBs, the so-called dioxin-like PCBs, behaves in the body like a dioxin. It is precisely this subgroup that dominates the endometriosis studies.

Which foods contain the most dioxins and PCBs?

In a Flemish survey, daily intake of dioxin-like compounds broke down as follows: fish and seafood contributed 25 to 43 percent, added fats 22 to 25 percent, dairy products 17 to 20 percent (PMID: 17720214). The pattern is stable, even though the absolute amounts have fallen since. The common denominator is fat of animal origin. Plant foods play almost no part in it.

How long do dioxins stay in the body?

A long time, and not the same length of time in every person. An analysis of more than 30 studies showed that the apparent half-life cannot be stated as a single fixed number. It depends on age, on body fat percentage, on smoking and on breastfeeding (PMID: 19337517). The honest order of magnitude is years to decades, depending on the congener. Anyone who reads a single number of years online is reading a simplification.

Was the monkey study really only about dioxin?

No, and that is the most important postscript to this story. In 2001 the serum of the same animals was measured 13 years after feeding had ended, and it contained not only TCDD but also 1,2,3,6,7,8-hexachlorodibenzofuran as well as PCB 77 and PCB 126. Disease severity correlated with the serum concentration of PCB 77 (PMID: 11134554). The feed was apparently contaminated with PCBs as well. The observation remains a signal, but it was not a clean experiment with a single substance.

What is TCDD, and why is it considered the most toxic dioxin?

TCDD stands for 2,3,7,8-tetrachlorodibenzo-p-dioxin. It is the best studied dioxin and serves as the reference point for the toxic equivalent, TEQ for short. Every other congener is given a factor expressing its potency relative to TCDD. TCDD itself has the factor 1. When you read a figure in picograms TEQ in a report, it is stated in this currency.

What is the aryl hydrocarbon receptor, and why is it not an estrogen receptor?

The aryl hydrocarbon receptor is a sensor for foreign substances. It sits inside the cell, binds certain molecules and then switches on genes, among them genes for enzymes that break foreign substances down. It is a switch of its own and not an offshoot of the estrogen system. In human endometrial cells, dioxin-like compounds activated the aryl hydrocarbon receptor without disturbing estrogenic processes in those cells (PMID: 20876610). That is why the term xenoestrogen is imprecise for dioxins.

What did the 1976 Seveso chemical accident contribute to endometriosis research?

At Seveso in northern Italy, an explosion at a chemical plant released large amounts of TCDD in 1976. Out of it grew the Seveso Women's Health Study, the cohort with the highest documented TCDD exposure of any population. Among 601 women, 19 cases of endometriosis were found. For serum levels above 100 ppt the relative risk ratio was 2.1, with a 90 percent confidence interval from 0.5 to 8.0, and no dose trend appeared (PMID: 12117638). A doubled risk that is not statistically secure. These data give no more than that.

Why do studies on dioxins and endometriosis reach different conclusions?

Because they measure different things. Some papers look at individual PCB congeners, others at summed values, others again at total TEQ. Some control groups were checked surgically, others were not. And because serum is usually drawn only after diagnosis, weight changes, periods of breastfeeding and the illness itself can influence the measurements. In Rome, clearly elevated odds ratios were found (PMID: 19654915), while in the US state of Washington, with 251 surgically confirmed cases, no consistent pattern emerged (PMID: 20423815). Both papers are carefully done.

Is dioxin exposure in Germany still a problem today?

It has become much smaller. In Swedish breast milk, the sum of PCDDs, the sum of dioxin-like PCBs and the total TEQ fell by 5.8 to 6.8 percent per year between 1972 and 2011, and in the final decade by 9.2 to 11 percent per year (PMID: 24080458). In France, dietary intake fell by a factor of 3.2 (PMID: 22487562). The Bavarian State Office for Health and Food Safety reports a decline of around 94 percent in bulk dairy milk since 1989. The burden has not disappeared, and for about ten years it has been stagnating at this low level.

What do the limit values say, and who sets them?

In Europe the assessment is made by the European Food Safety Authority. In 2018 it lowered the tolerable weekly intake to 2 picograms TEQ per kilogram of body weight per week, around seven times lower than the value that had applied before (DOI: 10.2903/j.efsa.2018.5333). The reasoning is remarkable: the critical endpoint of the calculation was sperm concentration, not endometriosis. So the authority takes these substances very seriously, it simply does so at a different place in the body.

Can I have my dioxin burden measured?

Technically yes, in everyday practice it is rarely useful. The analysis needs high-resolution mass spectrometry and a lot of sample material, it is laborious and hardly available outside research laboratories. Above all, the result changes little about what would follow from it. There is no treatment whose use depends on this value, and no study showing that lowering the value changes the course of endometriosis. What can sensibly be measured belongs in a conversation with your doctor.

Do I pass dioxins on to my child while breastfeeding, and should I therefore breastfeed less?

Fat-soluble pollutants do pass to the child through breast milk, that is not disputed. The National Breastfeeding Committee at the German Federal Institute for Risk Assessment and the professional societies still advise breastfeeding, in view of this pollutant burden too. A review from the predecessor institute of the German Federal Institute for Risk Assessment notes that the burden has fallen over the decades, that transfer before birth is considered more significant for the child's development than the time at the breast, and that the breastfeeding period accounts for only about 0.6 percent of the expected lifespan. The same paper does however put intake through breast milk in industrialised countries at ten to a hundred times the tolerable daily intake derived in 1998 (PMID: 11065082). Please do not make this decision on the basis of an article, but in conversation with your midwife or your doctor.

What do the endometriosis guidelines say about environmental toxins?

Little, and with good reason. The current German-language S2k guideline names polychlorinated biphenyls, bisphenol A and phthalates as isolated indications of environmental influences that may carry risk, while I did not find the word dioxin in the long version dated April 2025 (English-language journal version: PMID: 41684533). The European ESHRE guideline gives no recommendation on environmental factors at all (PMID: 35350465). The reason is not lack of interest. Guidelines recommend actions that have been tested, and an intervention study on lowering exposure does not exist.

I am trying to conceive. Should I lower my exposure first?

No, please not in that order. If you have been trying to conceive without success for some time, that belongs in a timely gynaecological assessment and, depending on the situation, a reproductive medicine assessment. Time is a real factor in this question, and this article is no reason to postpone an assessment. Whether anything changes for your fertility if you change your everyday life is something I cannot tell you, and I do not want to hold it out as a prospect either, because no intervention study on this exists. Letting both run side by side is the more honest path.

Should I change my hormone treatment because of this article?

No. Nothing in this article implies that you should stop, lower the dose of or pause the pill, a progestin preparation, a GnRH analogue, thyroid hormones, metformin or hormone replacement therapy. Every adjustment of a medication belongs in a medical conversation and needs medical supervision, even when it seems small to you. Bioidentical hormones are prescription medicines too, not gentle self-help. All of these medicines carry a risk side of their own, for example a raised thrombosis risk under combined hormonal contraceptives or a decrease in bone density under GnRH analogues. If you are unhappy with your treatment, that is a good reason for a conversation and not a reason to go it alone.

If I do everything right, will the endometriosis go away?

No, and I do not want to answer this question with a hope the data cannot carry. Endometriosis is a medical diagnosis with an established treatment, and gynaecological care remains the foundation. What you change about your environment replaces neither an assessment nor an indicated operation. It can be a second level on which you can do something, no more and no less. And nothing written here implies that every hormonal disturbance has an environmental cause.

Where this topic connects to the rest of your body

Dioxins and PCBs are one section of the picture. They stand alongside other groups of substances, alongside inflammatory status, alongside metabolism and alongside the question of what can sensibly be measured. Here are the connecting points.

If you want to understand the illness itself
Endometriosis: an integrative view

This article here deliberately does not explain the disease. There you will find its development, its diagnosis and the different levels in context.

If you want to know what else plays a part in daily life
Xenoestrogens in everyday life

The classic endocrine disruptors work through the estrogen receptor, dioxins do not. There you will find the other half of the story, from plastic to house dust.

If the comparison interests you
Zearalenone as a mycoestrogen

A mould toxin that, unlike dioxin, docks directly onto the estrogen receptor. The best contrast for grasping the difference between the two routes.

If mould is part of the picture
Mycotoxins: the basics

The second large group of persistent substances I ask about with hormonal complaints. What they are, where they come from, what is documented.

If you want to have an exposure measured
Measuring heavy metals in blood or urine

Why some exposures can sensibly be measured and others cannot, and which question should come before every lab request.

If you are pregnant or would like to be
Heavy metals in pregnancy and childhood

There you will find in detail why I am reserved on the subject of fish, and what counts especially in this phase of life.

If the breakdown routes interest you
Estrogen breakdown through the liver

CYP1A1 appears in this article as a target gene of the aryl hydrocarbon receptor. There you will find what role the same enzymes play in estrogen metabolism.

If you want to have your values determined
Hormone testing in women

Which test, which timing, how much it can tell you. The basis for everything discussed afterwards.

If your pattern looks like estrogen excess
Understanding estrogen dominance

The symptom pattern under which many women find this article. There it is about ratios rather than single values.

If the counterpart is missing
Recognising progesterone deficiency

Progesterone is the other half of the ratio. In endometriosis the tissue response to progesterone is often altered.

If inflammation and metabolism belong together
Insulin resistance and female hormones

The inflammation axis this article covers at length is closely tied to metabolism. There that connection is set out.

If another diagnosis is in the room
Understanding PCOS

The second large gynaecological diagnosis in which environment, inflammation and metabolism are discussed together.

If you want the whole picture
Why I look for environmental factors

Why I look for environmental factors in hormonal symptoms, along which grid, and when that search adds nothing.

If metals are part of the question
Heavy metals and female hormones

Cadmium as a metalloestrogen, lead and the bone store, and what blood, urine and hair analysis each show.

If the diagnosis is taking years
Endometriosis: why the diagnosis comes late

Why years often pass between the first symptoms and the diagnosis, and what ultrasound and MRI can do today.

If you want to place drinking water and cookware
PFAS: the forever chemicals

Why the forever chemicals stay in the body for years and where individual avoidance reaches its limit.

SJ

Shukri Jarmoukli

Physician · Area of focus: integrative medicine · ViveCura Berlin

I work in my private practice at the intersection of conventional medicine, functional medicine and Clinical Psychoneuroimmunology. With hormonal complaints I ask about housing, occupation, mould, exposure history and inflammatory status. That something can sometimes be found this way which can be addressed is an observation from my consultations and not a study result.

On this topic I am deliberately more reserved than many expect from an integrative practice. The link between dioxins, PCBs and endometriosis is mechanistically plausible and partly supported, it is not proven, and it does not explain the disease on its own. The gynaecological assessment remains the foundation. This article does not replace medical advice. It is meant to help you ask better questions at your next appointment.

ViveCura, Privatpraxis Shukri Jarmoukli, Skalitzer Straße 137, 10999 Berlin

Scientific sources

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Transparency on the evidence: where the data are thin
  1. The original study had seven animals per group. Every percentage from it is fragile. A single animal would have shifted the result by 14 percentage points.
  2. The exposure of these animals was not pure. PCB 77 and PCB 126 were detectable in serum. Which substance exactly was responsible for the finding has not been settled to this day.
  3. Seveso had 19 cases. A 90 percent confidence interval from 0.5 to 8.0 is compatible with almost any result. That is no evidence, neither for nor against.
  4. The two large case-control studies contradict each other. Rome positive, Washington negative. Both are properly done. They examined different congeners at different exposure levels and with different control groups.
  5. The meta-analyses show moderate heterogeneity. In the 2023 paper, I squared was 63 percent. In the strictest design the effect shrank to an odds ratio of 1.51.
  6. Exposure measured backwards is the most important methodological caveat. In case-control studies, serum is drawn after diagnosis. Weight changes, periods of breastfeeding and the illness itself can influence the values.
  7. There is no intervention study. Nobody has ever shown that lowering dioxin or PCB exposure changes the course or the occurrence of endometriosis. That is why no guideline can give a recommendation.
  8. Genetic detoxification variants explain nothing. The obvious idea that some women detoxify less well and therefore fall ill was systematically studied and not confirmed.
  9. Aromatase, HSD17B7, COX-2, MMP-2 and MMP-9 come from cell culture and animal models. Not one of these markers has been measured in humans as a response to a changed exposure.
  10. The source figures for fish, fats and dairy products come from Flanders in 2007 and were collected with a bioassay. They show the distribution of sources, not today's exposure level.
  11. Reference measures must not be mixed. The WHO factors of 1998 and of 2005 are not the same thing, a CALUX bioassay value is not directly comparable with either, and picograms per kilogram per day is something other than picograms per kilogram per week. On top of that comes the benchmark itself: the Irish, the French and the Flemish assessments were calculated against the old guidance value of 14 picograms per week, whereas since 2018 a value of 2 picograms applies in Europe.
  12. What deliberately does not appear here. No dosing recommendation, no elimination protocol, no product or test recommendation and no advice to change, reduce or end an existing treatment. Every adjustment of a medication needs medical supervision. Nothing in this article implies that a gynaecological assessment or an indicated operation should be postponed. What I describe from my consultations is marked as an observation and is not a study result.

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