Organotin levels in seafood and its implications for health risk in high-seafood consumers
Introduction
Occupational exposure represents the greatest exposure to organotin compounds (OTC). Food, especially fish and fishery products is considered to be the main sources. The main species are likely to be tri-substituted compounds (tributyltin TBT and triphenyltin TPT), which have been used extensively as biocides in wood preservatives, in antifouling paints for boats and as pesticides (ATSDR (Agency for Toxic Substances and Disease Registry), 2003, EFSA (European Food Safety Agency), 2004, Duft et al., 2005, AFSSA (Agence Française de Sécurité Sanitaire des Aliments), 2006). Mono- and di-substituted are generally used in mixtures in various amounts as polyvinyl-chlorides stabilizers (PVC). TBT compounds are on the list of priority substances in the field of water policy (EC, 2001). Antifouling paints have been restricted in many countries because of the recognized adverse effects of these compounds on both humans and aquatic ecosystems. Regulation 782/2003/EC bans the application of OTC on ships as from 7/1/2003 and to eliminate their presence on ships from 1/1/2008 (EC, 2003). Nevertheless, because these compounds are persistent in the environment and tend to accumulate through the food chain (Duft et al., 2005), reservoir sources may continue to contribute substantially to human exposure of these compounds for a long time.
Recently, many toxicological evaluations were published (WHO-IPCS, 1999a, WHO-IPCS, 1999b, WHO-IPCS, 2001, WHO-IPCS, 2006, ATSDR (Agency for Toxic Substances and Disease Registry), 2003, EC, 2004, EFSA (European Food Safety Agency), 2004, AFSSA (Agence Française de Sécurité Sanitaire des Aliments), 2006). A no observed adverse effect level (NOAEL) for immunotoxicity of 0.025 mg/kg bw/day was identified for TBT oxide from chronic feeding studies in rats (Vos et al., 1990, Cooke et al., 2004, Tryphonas et al., 2004). An oral reference dose (RfD), a guidance value for oral exposure, and an intermediate-duration oral minima risk level (MRL) of 0.0003 mg/kg/day for tributyltin oxide have been successively derived (US EPA, 1997; WHO-IPCS, 1999b, ATSDR (Agency for Toxic Substances and Disease Registry), 2003). An uncertainty factor of 100 was applied to the NOAEL (10 for animal to human extrapolation and 10 for human variability). Because tributyltin (TBT), dibutyltin (DBT), triphenyltin (TPT) and dioctyltin (DOT) exert their immunotoxic effects by similar mode of action and potency, it seemed reasonable to establish a group tolerable daily intake (TDI) for these OTC (EFSA (European Food Safety Agency), 2004, EC, 2004). 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 bw for TBT, DBT, TPT and DOT compounds was established (based on TBT oxide molecular mass, this group TDI is 0.1 μg/kg bw when expressed as Sn content or 0.27 μg/kg bw when expressed as TBT chloride). This group TDI seemed relevant by the AFSSA experts (AFSSA, 2006).
Even though some studies have recently estimated OTC exposure from ingestion of especially fish and shellfish (Cardwell et al., 1999, Kannan et al., 1995, Keithly et al., 1999, WHO-IPCS, 2001, Belfroid et al., 2000, SCOOP task 3.2.13, 2003, EFSA (European Food Safety Agency), 2004, OT-SAFE, 2004, Tesfalidet, 2004, Lee et al., 2005, FSA (Food Safety Agency), 2005, AFSSA (Agence Française de Sécurité Sanitaire des Aliments), 2006, Comprendo (Comparative Research on Endocrine Disrupters), 2006), the amount and percent of exposure from food in the French population has not been characterized well.
The aim of the present study is to compensate for this current situation. The food sample size is largely higher than in earlier studies and above all more representative of French high-consumers, as well as the consumption survey used to cross these occurrence data to estimate the exposure is much more accurate than those previously used. For the first time, this paper characterizes specifically the French population's OTC exposure of male and female adults (18–64 years), seniors (+ 65 years) and women of child-bearing age (18–44 years) from seafood.
Section snippets
Food consumption data
Nine hundred and ninety-six fish and fishery products adult high-consumers (at least two meals a week) aged 18 and over were recruited and selected (about 250 people per study zone, see Table 6) by using a validated food frequency questionnaire (FFQ) in four French coastal areas (Fig. 1) within a radius of 20–25 km around (Le Havre (English Channel), Lorient and La Rochelle (Atlantic Ocean), Toulon (Mediterranean Sea)). The distribution of individuals questioned within each region was
Occurrence data
Table 1 also presents the percentage of censored data corresponding to the percentage of data lesser than LOD. 11–15%, 47–52% or more than 90% data were censured for butyl-, phenyl- and octyltins, respectively. The low percentage of censored data clearly indicates that butyltins are generally mainly predominant in the samples analyzed, along with some phenyltins. The presence of octyltins was sporadic and comparable to SCOOP task apart from monooctyltin (MOT), detectable in 10% of all samples (
Acknowledgements
The authors would like to thank the General Directorate for Foods of the French Ministry of Agriculture and Fisheries for the grant. They also express their particular gratitude to C. Benoit-Bonnemason and H. Garraud, (UT2A, LCABIE, UPPA, Pau), P. Verger (Met@risk, INRA, Paris) and to all the participants in the CALIPSO survey.
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