Mudsnails and sediments from an electronic waste recycling region in South China were chosen to study the polybrominated diphenyl ethers (PBDEs) bioavailability of mudsnail in different ambient levels. Significant (p \ 0.05) correlations of biota-sediment accumulation factor (BSAF) versus the reciprocal of PBDE concentration in sediment (1/Sed) occurred in all quantitative PBDE congeners except BDE-209, showed that the BSAFs of PBDEs in mudsnails were increased with reciprocal increasing ambient levels. The BDE-183 correlation of mudsnail versus sediment (r = 0.580) was much lower than the correlation of BDE-209 versus BDE-183 in mudsnails (r = 0.812), indicated the main source of BDE-183 in mudsnails was from the debromination of higher brominated PBDEs.Keywords Polybrominated diphenyl ethers (PBDEs) Á Mudsnail Á Sediment Á Biota-sediment accumulation factor (BSAF) Polybrominated diphenyl ethers (PBDEs) are brominated flame retardants (BFRs) which are widely used as additive components in a range of consumer products, such as computers, televisions, textiles, furniture, and other building materials (Birnbaum and Staskal 2004). They can be dissolved in materials and then leached into the environment and entered biota (Strandberg et al. 2001). The electronic waste (e-waste) recycling especially uncontrolled dismantling aggravated the process (Julander et al. 2005). So PBDEs become ubiquitous in the environment (Ueno et al. 2004). Furthermore, most toxicological studies have shown that serious health consequences, such as thyroidogenic, estrogenic, and hepatic effects as well as neurodevelopmental disorders, could result from prolonged exposure to PBDEs (Darnerud et al. 2001). Two of the three commercial PBDE mixtures (''penta-BDE'' and ''octa-BDE'') have been banned by the European Union and several U.S. states. Currently, the ''deca-BDE'' commercial mixtures are still heavy used, and there is no regulation for the usage and disposal of deca-BDE.Because of their ubiquity and potential toxicity, fish (Johnson and Olson 2001), birds (Voorspoels et al. 2006), bird eggs (Jonathan et al. 2006), and other biota (Pettersson et al. 2004) had been used to monitor the distribution of PBDEs in the environment. It was reported that lower (tetra-and penta-) PBDEs accumulated and biomagnified in biota, while the higher congeners (deca-) were prevalent in aquatic environments and sediments (Martin et al. 2004). And dietary exposure studies revealed that the bioavailability of deca-BDE had produced a range of results (Huwe and Smith 2007). However, there are few studies on the PBDEs bioavailability of biomonitor under different ambient levels (Sellström et al. 1998). In this work, we chose mudsnails (Cipangopaludina cahayensis) and sediments from an e-waste recycling region in South China to study the PBDEs bioavailability of mudsnail in different ambient levels. We aimed the bioconcentration,
123Bull Environ Contam Toxicol (2009) 82:206-210 DOI 10.1007 congeners distribution and source of PBDEs in mudsnails and sedim...