Chemical Contaminants, Pathogen Exposure and General Health Status of Live and Beach-Cast Washington Sea Otters (Enhydra lutris kenyoni)
Brancato, M.S.1, L. Milonas1, C.E. Bowlby1, R. Jameson3 and J.W. Davis2
1 NOAA, Olympic Coast National Marine Sanctuary
2 U.S. Fish and Wildlife Service, Western Washington Fish & Wildlife Office
3 Retired, U.S. Geological Survey, Biological Resources Division
Analyses of blood and liver samples from live captured sea otters and liver samples from beach-
cast sea otter carcasses off the remote Washington coast indicate relatively low exposure to
contaminants, but suggest that even at the low levels measured, exposure may be indicated by
biomarker response. Evidence of pathogen exposure is noteworthy - infectious disease presents
a potential risk to Washington sea otters, particularly due to their small population size and
limited distribution. During 2001 and 2002, 32 sea otters were captured, of which 28 were
implanted with transmitters to track their movements and liver and blood samples were collected
to evaluate contaminant and pathogen exposure. In addition, liver samples from fifteen beach-
cast animals that washed ashore between 1991 and 2002 were analyzed to provide historical
information and a basis of reference for values obtained from live otters. The results indicate low
levels of metals, butyltins, and organochlorine compounds in the blood samples, with many of
the organochlorines not detected except polychlorinated biphenyls (PCBs), and a few aromatic
hydrocarbons detected in the liver of the live captured animals. Aliphatic hydrocarbons were
measurable in the liver from the live captured animals; however, some of these are likely from
biogenic sources.
A significant reduction of vitamin A storage in the liver was observed in
relation to PCB, dibutyltin and octacosane concentration. A significant and strong positive
correlation in vitamin A storage in the liver was observed for cadmium and several of the
aliphatic hydrocarbons. Peripheral blood mononuclear cell (PBMC) cytochrome P450 induction
was elevated in two of 16 animals and may be potentially related to aliphatic and aromatic
hydrocarbon exposure. Mean concentration of total butyltin in the liver of the Washington
beach-cast otters was more than 15 times lower than the mean concentration reported by Kannan
et al. (1998) for Southern sea otters in California. Organochlorine compounds were evident in
the liver of beach-cast animals, despite the lack of large human population centers and
development along the Washington coast. Concentrations of PCBs and chlordanes (e.g., trans-
chlordane, cis-chlordane, trans-nonachlor, cis-nonachlor and oxychlordane) in liver of
Washington beach-cast sea otters were similar to those measured in Aleutian and California sea
otters, excluding those from Monterey Bay, which were higher. Mean concentrations of 1,1,1,-
trichloro-2,2-bis(p-chlorophyenyl)ethanes (DDTs) were lower, and mean concentrations of
cyclohexanes (HCH, e.g., alpha BHC, beta BHC, delta BHC and gamma BHC) were slightly
higher in Washington beach-cast otters versus those from California and the Aleutians.
Epidemiologically, blood tests revealed that 80 percent of the otters tested positive for
morbillivirus and 60 percent for Toxoplasma, the latter of which has been a significant cause of
mortality in Southern sea otters in California. This is the first finding of positive morbillivirus
titers in sea otters from the Northeast Pacific. Individual deaths may occur from these diseases,
perhaps more so when animals are otherwise immuno-compromised or infected with multiple
diseases, but a population-threatening die-off from these diseases singly is unlikely while
population immunity remains high. The high frequency of detection of morbillivirus and
Toxoplasma in the live otters corresponds well with the cause of death of stranded Washington
sea otters reported herein, which has generally been attributable to infectious disease.
Washington's sea otter population continues to grow, with over 1100 animals currently inhabiting Washington waters; however, the rate of growth has slowed over recent years. The population has a limited distribution and has not yet reached its carrying capacity and as such, is
still considered at high risk to catastrophic events.
Keywords: sea otter, metals, butyltins, organochlorines, aromatic hydrocarbons, aliphatic
hydrocarbons, PCBs, infectious disease, Toxoplasma, morbillivirus, vitamin A, cytochrome
P450.
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