PCB concentrations in lake trout (Salvelinus namaycush) are correlated to habitat use and lake characteristics.

This study considers the importance of lake trout habitat as a factor determining persistent organochlorine (OC) concentration. Lake trout is a stenothermal, cold water species and sensitive to hypoxia. Thus, factors such as lake depth, thermal stratification, and phosphorus enrichment may determine not only which lakes can support lake trout but may also influence among-lake variability in lake trout population characteristics including bioaccumulation of OCs. A survey of 23 lakes spanning much of the natural latitudinal distribution of lake trout provided a range of lake trout habitat to test the hypothesis that lake trout with greater access to littoral habitat for feeding will have lower concentrations of OCs than lake trout that are more restricted to pelagic habitat. Using the delta13C stable isotope signature in lake trout as an indicator of influence of benthic littoral feeding, we found a negative correlation between lipid-corrected delta13C and sigmaPCB concentrations supporting the hypothesis that increasing accessto littoral habitat results in lower OCs in lake trout. The prominence of mixotrophic phytoplankton in lakes with more contaminated lake trout indicated the pelagic microbial food web may exacerbate the biomagnification of OCs when lake trout are restricted to pelagic feeding. A model that predicted sigmaPCB in lake trout based on lake area and latitude (used as proximate variables for proportion of littoral versus pelagic habitat and accessibility to littoral habitat respectively) explained 73% of the variability in sigmaPCBs in lake trout in the 23 lakes surveyed.

Toxaphene congeners in the Canadian Great Lakes basin: temporal and spatial food web dynamics.

Samples of a top predator fish species, lake trout (Salvelinus namaycush) and predominant forage species including smelt (Osmerus mordax), alewife (Alosa pseudoharengus), slimy sculpin (Cottus cognatus), deepwater sculpin (Myoxocephalus quadricornis) and lake herring (Coregonus artedii) were, collected from throughout 4 of the 5 Great Lakes (Superior, Huron, Erie and Ontario) (Fig. 1). Lake trout were also collected from three isolated lake systems (Lakes Nipigon, Simcoe and Opeongo), all located within the basin. All the samples were analysed for body burdens of total toxaphene and 22 toxaphene congeners. In addition, from each of the Great Lakes sites samples of major invertebrate dietary items, which included Mysis relicta, Diporeia hoyi and plankton, were similarly analysed. Whole lake trout samples, archived at -80 degrees C, were reanalysed to determine historical trends of toxaphene congeners plus carbon and nitrogen stable isotope signatures. The Lake Superior food web consistently had the highest levels of total toxaphene of all the Great Lakes monitored. The primary source of toxaphene to Lake Superior has been identified as atmospheric transport and deposition from sites in the southern US, Mexico and Central America (Hoff, R.M., Strachan, W.M.J., Sweet, C.W., Chan, C.H., Shackelton, M., Bidleman, T.F., Brice, K.A., Burnison, D.A., Cussion, S., Gatz, D.F., Harlin, K., Schroeder, W.H., 1996. Atmospheric deposition of toxic chemicals to the Great Lakes: A review of data through 1994. Atmospheric Environ. 30, 3505-3527). Of the offsystem lakes surveyed. Lake Nipigon, situated due north of Lake Superior and with a Lake Basin area of about 6% of Lake Superior (Hendendorf, C.E., 1982. J. Great Lakes Res. 8(3), 379-412) had total toxaphene levels in lake trout equivalent to about 50% of those found in lake trout from Lake Superior. Temporal trend toxaphene congener analysis was conducted on archived whole fish samples collected over the period 1980 through to the 1990's. Initially a nonachlorobornane congener (Parlar #50) was predominant, with congeners #40, #62 and #21 being the next most prominent in the 1980 samples. Samples from the 1990's showed a significant decline in the presence of lower chlorinated congeners #40 and #21. Analysis of total toxaphene in food webs, indicated elevated levels in lower trophic level species such as Diporeia and Cottus sp. which have a benthic association. The stable isotope temporal trend 13C signature identified a significant shift in the lake trout diet over the period 1993 to 1996.

The Great Lakes Fisheries Specimen Bank: a Canadian perspective in environmental specimen banking.

Since 1977 the Canadian Department of Fisheries and Oceans (DFO) has maintained a specimen bank for retrospective chemical analyses. The Great Lakes Fisheries Specimen Bank (GLFSB) is a complementary activity to the department's ongoing Great Lakes Contaminants Surveillance Program that has annually, since 1977, monitored levels of metals and organochlorines in aquatic biota throughout the Canadian Great Lakes. Past activities have focused on defining the effects of long-term frozen storage on the integrity of organochlorine residues in archived biological tissues. Archived samples have been reanalyzed for total PCBs, PCB congeners including co-planar PCBs, dioxin and furan isomers, and 22 toxaphene congeners. More recently, archived samples of predatory fish have been analyzed for stable isotopes of nitrogen (delta 15N) and carbon (delta 13C), as indicators of historical changes in food web dynamics. A catalogue or user-guide has recently been completed describing all information associated with samples stored in the GLFSB.

Baseline studies in the Slave River, NWT, 1990-1994: Part II. Body burden contaminants in whole fish tissue and livers.

The Northwest Territories section of the Slave River is the recipient of chemical compounds from a variety of sources, including upstream industry and agriculture. In 1990, concerned government agencies formulated a practical, focussed, and comprehensive environmental monitoring program to assess contamination in the river and the Slave River Environmental Quality Monitoring Program was established. The program was designed to respond to the distinct requirements of two major monitoring goals. The first priority was to ascertain whether the fish in the Slave River were safe to eat. The second goal was to establish a baseline data set with which to compare future effects from upstream activities and long-range transport of contaminants. From the data gathered in the present study, it appears that whole tissue of fish (muscle) is fit for human consumption. Throughout the monitoring period, consistently low concentrations of organochlorine pesticides, PCBs, dioxin and furan isomers, PAHs, chlorinated phenolics, and heavy metals have been observed and median concentrations have all been below federal fish consumption advisories. Also, the numerous data values below analytical detection limits attest to the relatively uncontaminated nature of the fish. These results were comparable with other studies conducted on arctic animals. The heavy metals observed in fish tissue are probably of natural origins, since inorganic analyses of suspended sediment in the Slave River indicated relatively elevated levels, with no known anthropogenic source. While the present study concluded that contaminant levels in whole fish are low, toxaphene levels in burbot livers should continue to be monitored since concentrations were consistently above fish consumption advisories during the monitoring and are eaten extensively by the native peoples. The second goal of the monitoring program was to develop a baseline data set and the values tabled in the current paper are useful in establishing a foundation for future comparison.