Organotin levels in seafood and its implications for health risk in high-seafood consumers

https://doi.org/10.1016/j.scitotenv.2007.08.027Get rights and content

Abstract

Fish and fishery products are considered as the main source of organotin compounds (OTC). Unfortunately, little national contamination data is available to assess food exposure of organotins from French consumers. To provide a more accurate estimate of risks to human health, the butyltin, phenyltin and octyltin compounds sampling in four French coastal areas were measured in 159 composite samples (96 fresh and frozen fish, 28 mollusks, 14 crustaceans, 1 echinoderm, 11 canned foods, 4 smoked fish, 5 prepared seafood-based dishes) by capillary gas chromatography coupled with a microwave induced plasma atomic-emission spectrometer (CGC–MIP-AES). In these samples, butyltins were usually predominant and the range of the contamination levels was generally below those of earlier studies (fish: mean 5.6; min–max 1.1–23 μg/kg; fishery products: mean 6; min–max 0.8–14 μg/kg). Fish, especially tuna, salmon, mackerel, saithe/coalfish and cod were largely the main contributors (38%) to the total organotin exposure. With the supplementary contribution of great scallop, surimi, squid and oysters, the exposure exceeded 50% in all. However, the utmost OTC exposure was lesser than 47% of the provisional tolerable weekly intake [EFSA (European Food Safety Agency). Opinion of the Scientific Panel on Contaminants in the food chain on a request from the Commission to assess the health risks to consumers associated with exposure to organotins in foodstuffs. (Question N°EFSA-Q-2003-110). The EFSA Journal, 102, 1–119, 2004. http://www.efsa.eu.int]. Nobody would exceed this limit. Finally, as this study has some limitations and since some other sources and health effects have not been clearly evaluated, it appears rational from public health and environmental viewpoints to continue to reduce the OTC levels in the environment.

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.

References (43)

  • Comprendo (Comparative Research on Endocrine Disrupters)

    Phylogenetic approach and common principles focussing on androgenic/antiandrogenic compounds

    Final publishable report: Executive summary on the project results. EU contract no. EVK1-CT-2002-00129

    (2006)
  • DevierM.H. et al.

    One-year monitoring survey of organic compounds (PAHs, PCBs, TBT), heavy metals and biomarkers in blue mussels from the Arcachon bay, France

    J Environ Monit

    (2005)
  • DuftM. et al.

    Biological impact of organotin compounds on mollusks in marine and freshwater ecosystems

    Coast Mar Sci

    (2005)
  • EC (European Commission)

    Decision No2455/2001/EC of 20 November 2001 establishing the list of priority substances in the field of water policy and amending Directive 2000/60/EC

    Official J

    (2001)
  • EC

    Commission Regulation (EC) No782/2003 of 14 April 2003 on the prohibition of organotin compounds on ships

    Official J

    (2003)
  • EC
  • EC

    Commission Regulation (EC) No78/2005 of 19 January 2005 amending Regulation (EC) No466/2001 setting maximum levels for certain contaminants in foodstuffs as regards heavy metals

    Official J

    (2005)
  • EFSA (European Food Safety Agency)

    Opinion of the Scientific Panel on Contaminants in the food chain on a request from the commission to assess the health risks to consumers associated with exposure to organotins in foodstuffs. (Question N°EFSA-Q-2003-110)

    The EFSA J

    (2004)
  • EN 13804

    Foodstuffs — determination of trace elements — performance criteria, general considerations and sample preparation

    European Committee for Standardization

    (2002)
  • EN 13805

    Foodstuffs — determination of trace elements — pressure digestion

    European Committee for Standardization

    (2002)
  • FentK.

    Ecotoxicology of organotin compounds

    Crit Rev Toxicol

    (1996)
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