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. Author manuscript; available in PMC: 2017 Feb 1.
Published in final edited form as: Environ Sci Pollut Res Int. 2015 Apr 1;23(3):2058–2080. doi: 10.1007/s11356-015-4383-0

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)
a

Elimination/depuration rate constants were determined for whole animals if not noted otherwise (please see the respective references for additional details);

b

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);

c

co-eluting with PCB 66;

d

co-eluting with PCB 133;

e

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);

f

co-eluting with PCB 92;

g

rainbow trout was fed a diet containing different levels of PCBs (Aroclor 1254) as well as six polychlorinated dibenzodioxins and dibenzofurans;

h

elimination rate constants summarize the range of elimination rate constants determined during summer, fall, winter, spring and annual temperature cycles;

i

co-eluting with PCB 153;

j

co-eluting with PCB 132,

k

elimination rate constants summarize the range of elimination rate constants determined at three different doses; NA = no apparent elimination. NS – regression analysis not significant.