Table 3.
Elimination (depuration) rate constants for selected C-PCBs and the persistent PCB 153 in selected fish species.
Species | Elimination (depuration) rate constant [10−2 day−1]a
|
Reference | |||||||
---|---|---|---|---|---|---|---|---|---|
PCB 84 | PCB 91 | PCB 95 | PCB 132 | PCB 136 | PCB 149 | PCB 153 | PCB 174 | ||
Arctic char (Salvelinus alpinus)b | 6.9 | 7.7 | 8.7 | 7.7 | 7.7 | (Wiberg et al. 2006) | |||
Eel (Anguilla anguilla) | 0.02 | NA | (de Boer et al. 1994) | ||||||
Flounder (Platichthys flesus) | 3.8 | 1.0 | (Goerke and Weber 2001) | ||||||
Guppy (Poecilia reticulata) | 0.34 | 0.41 | (Sijm et al. 1992) | ||||||
Rainbow trout (Oncorhynchus mykiss) | 0.3c | (−)-PCB 136: 0.14 (±)-PCB 136: 0.19 (+)-PCB 136: 0.27 |
(Wong et al. 2002a) | ||||||
Rainbow trout (Oncorhynchus mykiss)d | 0.5e | 0.4 | 0.4f | 0.5 | 0.5 | 0.4g | 0.4 | 0.4 | (Buckman et al. 2004) |
Rainbow trout (Oncorhynchus mykiss)h | 0.5e | 0.3 | 0.3f | 0.5 | 0.5 | 0.3g | 0.3 | 0.4 | (Buckman et al. 2004) |
Rainbow trout (Oncorhynchus mykiss)b | 0.8 | 0.5c | 0.9 | 0.8 | 0.6d | 0.5 | 0.5 | (Buckman et al. 2006) | |
Rainbow trout (Oncorhynchus mykiss) | 1.7 | 1.2 | 0.9 | (Konwick et al. 2006) | |||||
Rainbow trout (Oncorhynchus mykiss)e | 0.4–0.5f | 0.4–0.5 | 0.3–0.4c | 0.4–0.6 | 0.4–0.6 | 0.3–0.5d | 0.3–0.4 | 0.4–0.5 | (Buckman et al. 2007) |
Rainbow trout (Oncorhynchus mykiss)g | 0.9–1.6 | 1.2–2.0 | 1.3–1.9 | (Brambilla et al. 2007) | |||||
White prawn (Palaemon longirostris) | 29 | 1.7 | (Goerke and Weber 2001) | ||||||
Yellow perch (Perca flavescens)h | NA-1.4 | NA-1.4 | NA-1.3 | NA-1.1i | NA-1.0 | NA-1.0 | NA-1.1j | NA-1.0 | (Paterson et al. 2007) |
Zebrafish (Brachydanio rerio) | 1.6 | 1.0 | (Fox et al. 1994) | ||||||
Fathead minnow (Pimephales promelas) | 2.2 | NS | (Van Geest et al. 2011) | ||||||
Japanese koi (Cyprinus carpio)k | 0.06–0.51 | 0.76–1.1 | 0.34–0.66 | 0.36–0.69 | (Paterson et al. 2010) |
Elimination/depuration rate constants were determined for whole animals if not noted otherwise (please see the respective references for additional details);
rainbow trout was fed a diet containing Aroclor 1242, 1254 and 1260 (10 μg/g each) plus PCBs 202 and 209 (0.5 μg/g each);
co-eluting with PCB 66;
co-eluting with PCB 133;
rainbow trout was either treated with a PCB mixture containing Aroclor 1242, 1254 and 1260 (10 μg/g each) plus PCBs 202 and 209 (0.5 μg/g each) or this PCB mixture supplemented with (A) CYP 1A-inducing PCB congeners 77, 126 and 169 (10 ng/g each) or (B) CYP 2B-inducing PCB congeners 87, 99, 101, 153, 180 and 194 (10 ng/g each);
co-eluting with PCB 92;
rainbow trout was fed a diet containing different levels of PCBs (Aroclor 1254) as well as six polychlorinated dibenzodioxins and dibenzofurans;
elimination rate constants summarize the range of elimination rate constants determined during summer, fall, winter, spring and annual temperature cycles;
co-eluting with PCB 153;
co-eluting with PCB 132,
elimination rate constants summarize the range of elimination rate constants determined at three different doses; NA = no apparent elimination. NS – regression analysis not significant.