Endocrine disruption: thyroid system
EFSA completed a peer review in 2022 and concluded that thiabendazole meets the EU regulatory criteria for endocrine disruption in the thyroid. Animal studies consistently showed elevated thyroid-stimulating hormone, reduced triiodothyronine (T3), and follicular cell changes in the thyroid across multiple species and study designs. This was designated a critical area of concern under EU pesticide regulation.
Thiabendazole meets the criteria for endocrine disruption for humans in the thyroid modality, constituting a critical area of concern under Annex II of Regulation 1107/2009.
2022Regulatory reviewEFSA Journal, Peer review of the pesticide risk assessment for the active substance thiabendazole
Rat and dog studies showed elevated TSH, reduced T3 and increased thyroid weight at doses of 90 mg/kg per day and above, consistent with indirect stimulation of the thyroid gland leading to follicular cell proliferation.
1997AnimalJECFA Monograph 885, WHO Food Additives Series 39
Carcinogenicity
The US EPA classifies thiabendazole as likely to be carcinogenic to humans at doses high enough to disturb thyroid hormone balance, but not at lower doses. The carcinogenicity signal is mechanistically linked to the thyroid disruption rather than direct DNA damage. Thyroid follicular cell adenomas were observed in rat carcinogenicity studies and were considered part of the endocrine disruption evidence by EFSA.
The US EPA classifies thiabendazole as likely to be carcinogenic to humans at doses sufficient to cause a disturbance of thyroid hormone balance, but not likely to be carcinogenic at lower doses.
2002RegulatoryUS EPA Pesticide Fact Sheet, Thiabendazole (PC Code 060101)
Thyroid follicular cell adenomas observed in rat carcinogenicity studies were cited by EFSA as part of the thyroid-mediated endocrine disruption evidence base.
2022Regulatory reviewEFSA Journal, Peer review of the pesticide risk assessment for the active substance thiabendazole
Liver and blood effects
Studies in rats and dogs showed liver weight increases and signs of haemolytic anaemia at elevated doses. JECFA identified haematotoxicity (bone marrow and spleen changes consistent with anaemia) as the most sensitive endpoint and used it to set the ADI.
In rat and dog studies, histopathological changes in the spleen and bone marrow indicative of anaemia were the most sensitive endpoint identified, with a no-observable-effect level of 9 to 10 mg/kg per day.
2003AnimalJECFA Food Additives Series 49, TIABENDAZOLE (addendum), WHO
Liver hypertrophy and thyroid follicular cell hyperplasia were observed in rat subchronic studies at doses of 37 mg/kg per day and above.
1993AnimalJECFA Monograph 772, WHO Food Additives Series 31
Developmental toxicity
High-dose animal studies found skeletal malformations in mice and embryotoxicity in rabbits. These effects occurred at doses well above food residue exposure levels. JECFA set an overall developmental no-effect level at 24 mg/kg per day based on findings in rabbits and mice.
Developmental toxicity including skeletal malformations in mice and increased fetal resorption in rabbits was observed at high doses. The overall no-effect level for developmental effects was 24 mg/kg per day.
2003AnimalJECFA Food Additives Series 49, TIABENDAZOLE (addendum), WHO
Genotoxicity
Regulatory assessments by JECFA and the EU Pesticide Properties Database have recorded negative results in standard genotoxicity tests including bacterial mutation assays and mouse bone marrow tests. However, more recent in-vitro studies have found DNA strand breaks in human lymphocytes and mutagenic activity under UV light exposure, and one 2025 study reported mutagenic effects in bacterial testing. The evidence is conflicting and the regulatory consensus has not yet incorporated the newer findings.
Standard genotoxicity tests including chromosome aberration, DNA damage, and gene mutation assays returned negative results in regulatory evaluations.
2024RegulatoryPesticide Properties DataBase (PPDB), University of Hertfordshire
A 2025 study found thiabendazole induced frameshift and base-pair mutations in bacterial Ames testing and caused dose-dependent DNA strand breaks in human lymphocytes in a comet assay.
2025LabPMC11989162, Possible Genotoxic Effects of Post-Harvest Fungicides Applied on Citrus Peels, PMC
Consumer exposure from treated fruit
Thiabendazole concentrates in the peel. UK pesticide monitoring found thiabendazole in grapefruit at 2.4 mg/kg in 2024. The UK Health and Safety Executive calculated that peeling the fruit before eating leaves only 5% of the residue in the flesh, bringing intake within safety margins. Eating peel on its own, or for infants specifically, brings exposure closer to the acute reference dose.
In Q1 2024, the UK pesticide residues programme detected thiabendazole in grapefruit at 2.4 mg/kg. HSE risk assessment found no exceedance of the ARfD when the peel is removed, but infant exposure including peel reached 131% of the ARfD in a worst-case analysis.
2024ObservationalUK Government Quarter 1 2024 Pesticide Residues Monitoring Programme, HSE