Estimates of trace metal bioavailability to humans ingesting contaminated oysters
Introduction
Oyster farming is the primary aquaculture process in France with a production of approximately 130 000 tonnes/year. Thus France is the leading oyster producer in Europe, and among the first four oyster-producing countries in the world (Comité National de la conchyliculture, 2002). Oyster aquaculture represents a very important market which earns 460 millions Euros each year in France (IFREMER, 2002). The safety of food to the consumer is a major concern for our society. Correspondingly there are standards that are intended to ensure the safety of consumers of trace metals in shellfish, by laying down maximum permitted contents of potentially toxic elements therein. Food is considered as unfit for human consumption if it contains trace metal concentrations above these permitted standards. For example, the maximum permitted concentration of cadmium in oysters is 1 mg/kg fresh weight (European Communities, 2001). However, such standards are expressed as total concentrations of metals, whereas the bioavailability of the constituent metals and thus their potential transfer in the trophic web will vary according to the physico-chemical form (speciation) of accumulated storage in the oysters, and their potential breakdown during the digestive process. Until recently it has been particularly the metals present in the soluble fraction of food (prey) items which have been considered as bioavailable to the consumer, but some authors have also studied the bioavailability of metals present in insoluble fractions (Reinfelder and Fisher, 1994; Wang and Fisher, 1996; Wallace and Lopez, 1996, Wallace and Lopez, 1997; Wallace et al., 1998; Wallace and Luoma, 2003). Ettajani and Amiard (1995) showed that, in vitro, acid or enzymatic attacks on organic matter play a dominant role in the release of copper, cadmium and silver. This in vitro process is a model of the process of human digestion, brought about by enzymes (pepsin, chymotrypsin, lipase, trypsin, etc.) combined with various pHs (Ettajani and Amiard, 1995). In the human stomach, the pH of the secretions is lower than 1 but according to Rieutort (1999), after dilution with foods and saliva the pH of the bolus reaches between 2 and 4. This acid pH is likely to be a cause of the mobilisation of metals from the insoluble fraction of food, thereby increasing their bioavailability to the consumer.
The aim of this study was to provide a realistic estimate of the bioavailability, during the gastric digestion, of four trace metals (Ag, Cd, Cu and Zn) in oysters, so that the food standards to be applied to oysters can be set to not only protect consumers but also to avoid unnecessary penalisation of oyster companies. All of these four trace metals have the potential to be toxic above threshold availability, even though copper and zinc are essential to life in low concentrations.
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Biological material
Oysters Crassostrea gigas were sampled from Bourgneuf Bay near the Loire estuary (France), considered as a clean site (Table 1). Then oysters were transplanted for 6 months (May 1999–October 2000) along the French Atlantic coast to various sites:
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Arcachon Bay, which is an important larval rearing area for oysters, another clean site (Table 1).
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Pen Bé, also clean area (Table 1).
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Ronce les Bains, a moderately contaminated site (Table 1).
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The Gironde estuary, a contaminated zone particularly for
Distribution of metals between the soluble and the insoluble fractions
The average percentages of the concentration of each metal in the soluble (S1) and insoluble fractions (P1) according to the sites are shown in Fig. 2. The relationships of soluble and insoluble concentrations of silver, cadmium, copper and zinc, with the total concentrations of each metal are shown in Fig. 3.
Silver is for the most part in insoluble form (59–90%) whatever the site considered (Fig. 2a). When the total silver concentration increases, it is essentially in the insoluble form (Fig.
Discussion
The physicochemical form of a trace metal in food plays an important role in determining the bioavailability of dietary metal in the digestive tract of the consumer, and hence how much metal is transferred to the next trophic level. It is important therefore to determine the distribution of accumulated metals in food organisms into soluble and insoluble components, and to model the digestibility of the insoluble form. This has been achieved for oysters in this study.
The importance of the
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