Se. Koslowski et al., THE DISTRIBUTION OF 42 PCBS, INCLUDING 3 COPLANAR CONGENERS, IN THE FOOD-WEB OF THE WESTERN BASIN OF LAKE ERIE, Journal of Great Lakes research, 20(1), 1994, pp. 260-270
Non-ortho substituted PCBs, IUPAC numbers 77, 126, and 169, along with
39 other PCB congeners were quantified in samples of Lake Erie sedime
nt and biota during the summer of 1991. Many PCB congeners were found
at elevated levels, and biomagnification was apparent in all congeners
but was more predominant in congeners with relatively high octanol-wa
ter partition coefficients (log K(ow) > 6.0). PCA analysis suggested t
hat most PCB congeners had similar distributions in the Lake Erie food
web, although congeners with very high Kows and coplanar congeners IU
PAC # 77, 126, and 169 were found to have different distributions. Non
-parametric statistics were used to determine if significant differenc
es in concentration of selected PCB congeners existed among species an
d among tissues. Congener 126 was found primarily in benthic fish and
top predators, whereas there was no significant differences in the con
centrations of congener 77 in fish species of the benthic and pelagic
food web. Congener 169 was found at very low concentrations in the foo
d web of Lake Erie. There were also significant differences in concent
rations of coplanar PCBs among liver, egg, and muscle tissues, but tre
nds were not consistent among all the species examined. As significant
differences were observed in the distribution of PCB congeners in the
Lake Erie food web ''total PCB'' might not be an adequate estimation
of the toxicological hazards associated with PCB accumulation. It is e
vident that the dynamics of individual congeners, in particular the co
planar PCBs, need to be accurately assessed in order to predict the en
vironmental hazard of PCBs.