Periodic Reporting for period 3 - FREIA (Female Reproductive toxicity of EDCs: a human evidence-based screening and Identification Approach)
Reporting period: 2022-01-01 to 2023-06-30
We previously showed that endpoints that are currently being assessed in rat studies in regulatory testing are not sufficiently sensitive to detect an endocrine disrupting effect. Our studies did reveal some findings that may improve existing test guidelines:
- Our data show that mammary glands shortly after birth (postnatal day 6) and in young adult (postnatal day 22) rats exposed in the womb to DES and KTZ were different compared to mammary glands of unexposed pups. Together with the platform for international standard-setting Organisation for Economic Co-operation and Development (OECD), we are assessing if inclusion of mammary gland analysis in existing test guidelines is valid and feasible.
- In test guidelines, effects on rat ovaries are evaluated by traditional histological assessment. We explored the possibility to use a relatively quick screening process called surface photo counting (SPC). Our data show that the SPC method has good predictive value in the assessment of ovulations and is simpler, faster, and more cost-effective than traditional histological assessment. SPC might open new possibilities for a fast and operator-friendly assessment of effects on ovaries that can help to prioritize exposure groups for more thorough histological evaluation (doi: 10.1016/j.reprotox.2023.108416).
- We evaluated whether circulating steroid hormones may be an indicator of EDC effects. Clear age-dependent changes in hormone levels were observed in plasma of rats. However, exposure to KTZ and DES in the womb did not result in changes in circulating steroid hormone levels in female rats after birth. These data do not support inclusion of circulating sex steroid hormones in test guidelines. This does not mean that effects of chemicals on steroid hormone formation are irrelevant. In contrast, many of the effects of EDCs observed in our cell models revealed changes in steroid hormone formation, indicating an effect on reproductive cells directly. Our data do not indicate that an ovarian-specific cell model would improve EDC identification, but the existing steroidogenesis assay H295R may be improved by measuring more steroid hormones. Under supervision of the OECD, we are performing a study with other labs to investigate this.
Ultimately, we aim to integrate our newly identified biomarkers and sensitive endpoints with existing test systems from OECD to improve on future test methods and a strategy to determine the effect of an EDC on female reproductive development and health.
To provide further evidence on the effects of EDCs on female fertility, we explored this association in women attending fertility clinics in Sweden and Estonia. Levels of 59 known and suspected EDCs were analysed in follicular fluid, the biological fluid surrounding oocytes, of 185 Swedish women and 148 Estonian women undergoing fertility treatment. Multiple chemicals were detected in all follicular fluids. In >90% of the follicular fluids, 3 metabolites of the phthalate DEHP, methylparaben, and 6 PFAS (PFOS, PFOA, PFHxS, PFUnDA, PFNA and PFDA) were detected and used to link with female fertility parameters. The ovaries of women with higher levels of DEHP, methylparaben and possibly PFUnDA and PFOA responded less to fertility treatment, established by calculating the ovarian sensitivity index (OSI). There were indications that some PFAS lowered the success of fertility treatment, determined by chance of establishing a pregnancy or live birth. Overall, this study provides additional evidence that DEHP can negatively influence female fertility. In addition, several other chemicals, i.e. methylparaben and some PFAS, were identified that may harm ovarian function and contribute to female infertility (doi.org/10.1016/j.envres.2022.114447). We also studied how these women were exposed to these chemicals. The Swedish women from this study answered a questionnaire that contained information on home-environment, occupation, lifestyle and diet. We found that frequent use of perfumes was associated with higher phthalate (MEP) levels. Henn’s egg consumption led to higher PFAS exposure. PFAS levels were also associated with certain fish consumption. We did not observe any correlation between the semi-persistent chemicals and use of plastics in microwave heating of food or flooring material (doi.org/10.1038/s41370-023-00579-1). We are currently collecting available scientific data on how humans, and women in particular, can be exposed to EDCs and what actions effectively can be taken to avoid exposure.
On the FREIA website (www.freiaproject.eu) general background information on EDCs and female reproductive health can be found as well as project specific information, including webinar recordings, peer-reviewed scientific publications and databases, the FREIA factsheet and infographics. FREIA is one of the eight projects on test method development for EDC identification within the EURION cluster (www.eurion-cluster.eu).