Salvelinus namaycush

Campbell LM, DCG Muir, DM Whittle, S Backus, RJ Nostrum, AT Fisk (2003) Hydroxylated PCBs and other chlorinated phenolic compounds in lake trout (Salvelinus namaycush) blood plasma from the Great Lakes region. Environ Sci Technol 37 1720-1725. 

McMurtry MJ, Wales DL, Scheider WA, Beggs GL, Dimond PE. 1989. Relationship of mercury concentrations in lake trout (Salvelinus namaycush) and smallmouth bass (Micwpterus dolomieui) to the physical and chemical characteristics of Ontario lakes. Can J Fish Aquat Sci 46 426 34. 

Lake trout, Salvelinus namaycush Lake Cayuga, New York, whole ... 

Tong, S.S.C., W.D. Youngs, W.H. Gutenmann, and D.J. Lisk. 1974. Trace metals in Lake Cayuga lake trout (Salvelinus namaycush) in relation to age. Jour. Fish. Res. Board Canada 31 238-239. 

Common carp, Cyprinus carpio recently-fertilized eggs exposed to 25-186 pg/L at pH 7.5 or 5.6 Lake trout, Salvelinus namaycush At pH 7.5, lead increased heart rate and decreased body movements. At pH 5.6 there was a dose-dependent reduction in survival and increase in spinal cord deformities 42... 

Borgmann, U. and D.M. Whittle. 1991. Contaminant concentration trends in Lake Ontario lake trout (Salvelinus namaycush) 1977 to 1988. Jour. Great Lakes Res. 17 368-381. 

Futter, M.N. 1994. Pelagic food-web structure influences probability of mercury contamination in lake trout (,Salvelinus namaycush). Sci. Total Environ. 145 7-12. 

DeVault, D.S., W.A. Willford, R.J. Hesseberg, D.A. Nortrupt, E.G.S. Rundberg, A.K. Alwan, and C. Bautista. 1986. Contaminant trends in lake trout (Salvelinus namaycush) from the upper Great Lakes. Arch. Environ. Contam. Toxicol. 15 349-356. 

Lake trout, Salvelinus namaycush Fertilized eggs were exposed for 48 h to graded concentrations (0, 0.1, 1, 10, or 100 ng 2,3,7,8-TCDD/L) to achieve egg concentrations of 0, <15, 40, or 400 ng 2,3,7,8-TCDD/kg FW egg. Eggs were then transferred to flowing uncontaminated media through hatch... 

Spitsbergen, J.M., M.K. Walker, J.R. Olson, and R.E. Peterson. 1991. Pathologic alterations in early life stages of lake trout, Salvelinus namaycush, exposed to 2,3,7,8-tetrachlorodibenzo-p-dioxin as fertilized eggs. Aquat. Toxicol. 19 41-72. 

Whyte, J.J., M.R. van den Heuvel, J.H. Clemons, S.Y. Huestis, M.R. Servos, D.G. Dixon, and N.C. Bols. 1998. Mammalian and teleost cell line bioassay and chemically derived 2,3,7,8-tetrachlorodibenzo-jo-dioxin equivalent concentrations in lake trout (Salvelinus namaycush) from Lake Superior and Lake Ontario, North America. Environ. Toxicol. Chem. 17 2214-2226. 

Toxaphene elimination rates vary between species. In rats, the half-time persistence of toxaphene (time to 50% excretion = Tb 1/2) was 1 to 3 days (USEPA 1980a). If the trend persisted, virtually all toxaphene would be eliminated in five half-lives. Elevated blood toxaphene levels in a human subject who had eaten catfish fillets containing 52 mg of toxaphene/kg dropped 67% in 11 days. By 14 days after the initial measurement, toxaphene blood levels were below analytical detection limits (USEPA 1980a). Persistence seems to be longer in some fishes. Lake trout (Salvelinus namaycush) given a single intraperitoneal injection of 7 mg toxaphene/kg BW had a Tb 1/2 of 322 days for white suckers (Catostomus commersoni), this value was 524 days (Delorme et al. 1993). 

Harrison, S.E., J.F. Klaverkamp, and R.J. Hesslein. 1990. Fates of metal radiotracers added to a whole lake accumulation in fathead minnow (Pimephales promelas) and lake trout (Salvelinus namaycush). Water Air Soil Pollut. 52 277-293. 

Seven species of teleosts (channel catfish, Ictalurus punctatus bluegill, Lepomis macrochirus coho salmon, Oncorhynchus kisutch rainbow trout, Oncorhynchus mykiss fathead minnow, Pimephales promelas brook trout, Salvelinus fontinalis lake trout, Salvelinus namaycush)... 

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