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Which information identifies a chemical as endocrine disrupting?
Poul Bjerregaard Institute of Biology University of Southern Denmark Odense and Danish Centre on Endocrine Disrupters UNEP EDC Advisory Group meeting, Geneva , September 25-26, 2015
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WHO EDC definition Endocrine mechanism Adversity
Plausible link between the two
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Adversity according to WHO/IPCS 2004
A change in morphology, physiology, growth, reproduction, development or lifespan of an organism which results in impairment of functional capacity or impairment of capacity to compensate for additional stress or increased susceptibility to the harmful effects of other environmental influences
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Adversity? Risk assessment of chemicals What do we want to protect?
Human risk assessment: Every individual Environmental risk assessment: The structure and function of the ecosystem
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Environmental risk assessment
Protection of ecosystem structure and function The aim is to protect 95% of the species ‘Adversity ’defined from population effects Not effects on the individual
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Environmental risk assessment
Protection of ecosystem structure and function The aim is to protect 95% of the species ‘Adversity’ defined from population effects Not effects on the individual
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Relevant OECD test guidelines
Human risk assessment TG 416 or 433 (mammals) E.g. malformed male genitals, altered AGD Environmental risk assessment TG 234 Fish Sexual Development Test
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Fish Sexual Development Test
Altered content of yolk proteins Controlled by oestrogen Indicates endocrine mechanism - not adversity Altered sex ratio Indicates endocrine mechanism and adversity OECD Guidance Document 150
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Danish suggestion for EDC-criteria
Category 1 – Endocrine Disrupter Adverse in vivo effects ED mode of action in vivo clearly linked to adverse in vivo effects Category 2a – Suspected Endocrine Disrupter Adverse effects in vivo where an ED MoA is suspected ED MoA in vitro combined with toxicokinetic in vivo data ED MoA in vivo suspected to be linked to adverse effects in vivo Category 2b – Indicated Endocrine Disrupter in vitro/in silico evidence indicating potential for ED in vivo
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Exemplified by chemical UV filters
Category 2a Category 1 Danish 2012-assessment BP-3: Indications of oestrogenic and anti-androgenic effects. Not consistent Category 2a Category 2a TG234 needed
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Sexual development in zebrafish
♀ ♂ Hatch 20 days 40 days 60 days
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Sex ratio altered – more ♀
Kinnberg et al Environ.Toxicol.Chem. In press.
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No consistent effect on yolk proteins
12 d exposure
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Conclusion Exposure to benzophenone 3 skews sex ratio
so Benzophenone 3 is an EDC
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Is BP-3 oestrogenic or anti-androgenic?
Does it matter ? Depends on the requirement for detailed knowledge about the mechanism of action Detailed knowledge about ‘Adverse Outcome Pathways’ is desirable But not always obtainable
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A chemical may have multiple AOPs
Prochloraz Fungicide
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Prochloraz: More male zebrafish
* 100 Female Male Intersex Undifferentiated 80 60 % 40 20 73 72 72 69 Control 16 m g/l 64 m g/l 202 m g/l Prochloraz Prochloraz Prochloraz Kinnberg et al Comp. Biochem. Physiol.145C,
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Prochloraz is anti-androgenic in rats
Laier et al Toxicol.Appl.Pharmacol. 213,
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Effect of prochloraz Cholesterol Prochloraz Anti-androgenic in rats
Testosterone Prochloraz Inhibits aromatase in zebrafish (?) Oestrogen
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Conclusion Detailed knowledge on ‘Adverse Outcome Pathways’ is not necessarily needed to reach conclusions on endocrine disrupting activity
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