The
trophodynamics of halogenated flame retardants (HFRs) including
polybrominated diphenyl ethers (PBDEs) and alternative HFRs were investigated
in the terrestrial, vegetation–caribou–wolf food chain
in the Bathurst Region of northern Canada. The greatest concentrations
in vegetation (geometric mean of lichens, moss, grasses, willow, and
mushrooms) were of the order 2,4,6-tribromophenyl allyl ether (TBP-AE)
(10 ng g–1 lw) > BDE47 (5.5 ng g–1 lw) > BDE99 (3.9 ng g–1 lw) > BDE100 (0.82
ng
g–1 lw) > 1,2,3,4,5-pentabromobenzene (PBBz)
(0.72
ng g–1 lw). Bioconcentration among types of vegetation
was consistent, though it was typically greatest in rootless vegetation
(lichens, moss). Biomagnification was limited in mammals; only BDE197,
BDE206–208 and ∑PBDE biomagnified to caribou from vegetation
[biomagnification factors (BMFs) = 2.0–5.1]. Wolves biomagnified
BDE28/33, BDE153, BDE154, BDE206, BDE207, and ∑PBDE significantly
from caribou (BMFs = 2.9–17) but neither mammal biomagnified
any alternative HFRs. Only concentrations of BDE28/33, BDE198, nonaBDEs,
and ∑PBDE increased with trophic level, though the magnitude
of biomagnification was low relative to legacy, recalcitrant organochlorine
contaminants [trophic magnification factors (TMFs) = 1.3–1.8].
Despite bioaccumulation in vegetation and mammals, the contaminants
investigated here exhibited limited biomagnification potential and
remained at low parts per billion concentrations in wolves.