TABLE G2.
Literature data on occurrence of TBBPA derivatives (TBBPA‐bMeE and TBBPA‐bDiBPrE) in food samples from European countries.
| Derivative | Country | Year | Food matrices analysed | Food matrices TBBPA derivative detected (detection frequency) | Mean (range) | Reference |
|---|---|---|---|---|---|---|
| General food categories | ||||||
| TBBPA‐bMeE | France | 2014–2016 |
Food samples Fish, Crustaceous/molluscs, Milk, Egg, Sheep liver, Meat N = 577 (feed excluded) |
Fish (22/114) Crustaceous/molluscs (83/154) Milk (1/72) Egg (1/57) Sheep liver (0/28) Meat (1/152) |
< LOD (< LOD–3) ng/kg ww < LOD (< LOD–90) ng/kg ww < LOD (< LOD–0.04) ng/kg ww < LOD (< LOD–0.069) ng/kg ww – < LOD (< LOD–0.077) ng/kg ww LODs not reported. LOQ = 0.4 ng/kg (as reported by Bichon et al., 2018) |
Venisseau et al. (2018) |
| TBBPA‐bDiBPrE | France | 2014–2016 |
Food samples Fish, Crustaceous/molluscs, Milk, Egg, Sheep liver, Meat N = 577 (feed excluded) |
Fish (22/114) Crustaceous/molluscs (8/154) Milk (1/72) Egg (1/57) Sheep liver (0/28) Meat (3/152) |
< LOD (< LOD–300) ng/kg ww < LOD (< LOD–1700) ng/kg ww < LOD (< LOD–4.41) ng/kg ww < LOD (< LOD–9.49) ng/kg ww – < LOD (< LOD–11.51) ng/kg ww LODs not reported. LOQ = 21 ng/kg (as reported by Bichon et al., 2018) |
Venisseau et al. (2018) |
| Fish and seafood | ||||||
| TBBPA‐bMeE |
EU area Six sites: The Netherlands, Sweden, UK (2 sites), France, Germany |
2007–2013 |
Fish (freshwaters and estuaries) Bream (Abramis brama) from all sites and sole (Solea solea) only from the Netherlands N = 43 |
All concentrations < 0.4 μg/kg (LOD) | Kotthoff et al. (2017) | |
| TBBPA‐bDiBPrE | Italy | 2010 |
Liver of fish (freshwater) 4 common carps (Cyprinus carpio), 2 breams (Abramis brama), 3 sanders (Sander lucioperca) and 3 sheatfishes (Silurus glanis) |
All concentrations < LOD: 0.66 μg/kg dw | Viganò et al. (2015). Emerging and priority contaminants with endocrine active potentials in sediments and fish from the River Po (Italy). Environmental Science and Pollution Research, 22, 14050–14066 | |
| TBBPA‐bDiBPrE | Italy | 2010 |
Clams N = 327 |
All concentrations < LOD: 0.66 μg/kg dw | Casatta et al. (2015). Tracing endocrine disrupting chemicals in a coastal lagoon (Sacca di Goro, Italy): Sediment contamination and bioaccumulation in Manila clams. Science of the Total Environment, 511, 214–222 | |
Abbreviations: dw, dry weight; LOD, limit of detection; LOQ, limit of quantification; MB, medium bound; UB, upper bound; ww, wet weight.