SUMMARYThe Panel was asked to assess the possible risks to human health from the consumption of food contaminated with organotin compounds (OTC), based on intake estimates for Europe. The main source of OTC in food is likely to be tri-substituted compounds (e.g. tributyltin (TBT) and triphenyltin (TPT)), which have been used extensively as biocides in wood preservatives, in antifouling paints for boats and as pesticides. Mono-and di-substituted OTC (e.g. monomethyltin (MMT), dimethyltin (DMT), dibutyltin (DBT), mono-n-octyltin (MOT) and di-n-octyltin (DOT)) are generally used in mixtures in various amounts as polyvinyl chlorides (PVC) stabilizers, and dialkyltins have been approved as PVC stabilisers for food contact materials. OTC are lipophilic contaminants sparingly soluble in water and easily adsorbed to particulate matter in the aquatic environment. Hence, they accumulate in sediments where they are relatively persistent and can be taken up by benthic organisms such as clams. OTC tend to accumulate in fish and other aquatic organisms. There is indication that not only in laboratory animals but also in humans OTC are absorbed from the gastrointestinal tract and that triorganotins are bio-degraded to di-and monoorganotin compounds.The Panel focused on the most toxic OTC: TBT, DBT and TPT, primarily found in fish and fishery products and for which the exposure databases were considered adequate. Furthermore, the Panel considered it appropriate to assess also the toxicity of DOT as they act by a similar mode of immunotoxic action, even though not found in fish and fishery products. In particular, TBT and TPT are highly toxic to aquatic organisms and show a complex toxicity profile in rodents. Furthermore, they tend to bioaccumulate through the food chain (in particular in fish and seafood). TBT and TPT cause masculinization in female snails ("imposex") and in fish at low concentrations (1 ng/L in water), suggesting that these compounds are endocrine disruptors. Reproductive and developmental toxicity in rodents at relatively low doses (around 1 mg/kg b.w./day) further supports this endocrine activity. The critical toxicological endpoint for risk assessment was considered to be immunotoxicity. Other endpoints of toxicological relevance considered in this opinion are reproductive and developmental toxicity, genotoxicity, carcinogenicity, and neurotoxicity. A no observed adverse effect level (NOAEL) for immunotoxicity of 0.025 mg/kg b.w./day was identified for TBT oxide from chronic feeding studies. Because TBT, DBT, TPT and DOT exert their immunotoxic effects by similar mode of action and potency, the Panel considered it reasonable to establish a group tolerable daily intake (TDI) for these OTC. In the absence of specific studies on combined effects it seemed justified to consider the immunotoxic effects of these compounds as additive. By applying a safety factor of 100, a group TDI of 0.25 µg/kg b.w. for TBT, DBT, TPT and DOT compounds was established (based on TBT oxide molecular mass, this group TDI is 0.1 µg...