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Lara
Dehn was first funded by our sister program, Alaska
EPSCoR. She has done work with their Outreach
Program and now, she is one of our Internal Awards Graduate Fellowship
Recipients.
Feeding ecology of Arctic marine biota as determined by heavy metal dynamics
Project description
The objectives of this study are to develop a
better understanding of biomagnification of selected heavy metals in the Arctic
marine food web, to determine trophic level effects of these metals to aid in
delineation of contaminant pathways and to establish baseline values for subsistence
harvested marine mammals in Alaska. It is hypothesized, that heavy metals can
be discriminators for prey as well as ecological relationships in the Arctic.
It is widely recognized that trophic position is tightly linked
to contaminant accumulation. However, the accumulation of certain metals seems
to be associated with the prey consumed or the feeding habitat rather than trophic
level. It has been shown, that cadmium (Cd) concentrations in the kidney of
bowhead whales (Balaena mysticetus) are higher than in some top level
consumers even though this species feeds on pelagic krill (Woshner et al., 2001a;
Bratton et al., 1997). It is likely that whales and other marine mammals are
therefore exposed to elevated concentrations of heavy metals in their diet and
that diet selection of these animals will influence metal distribution in tissues.
For this study, liver, kidney and muscle (and epidermis in the case of whales)
have been collected from a variety of Arctic marine mammals in northern Alaska
and Canada as well as potential prey items. All tissues will be analyzed for
total mercury (THg) and methyl mercury (MeHg), as well as selenium (Se), cadmium
(Cd), silver (Ag), copper (Cu) and zinc (Zn). Stable isotopes d13C and d15N
and stomach contents analysis are used as trophic level discriminators to evaluate
bioaccumulation, trophic transfer and pathways of these heavy metals in the
Arctic marine food web.
Poster session - materials presented
at the AAAS (September 19-20,2002)
Click on graphs below to see a larger version in another
window.
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Fig. 1 a & b show age versus stable nitrogen and carbon isotopes in ringed seals (Holman and Barrow) and bearded seals. d15N displays a wide range with no significant difference between ringed (Holman and Barrow) and bearded seals, indicating a similar trophic position. The observed variation likely displays diverse feeding habits in bearded seals and dependence on either krill or Arctic cod in ringed seals. d13C is significantly more enriched in benthic feeding bearded seals than ringed seals. Seals harvested in Canada are significantly more depleted in stable carbon isotopes than Alaskan seals. |
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| Fig 2 a & b show significant differences in total mercury (THg) and methyl mercury to THg ratio (%MeHg) in ringed, bearded and spotted seal liver. Piscivorous spotted seals have the lowest THg concentrations, but the highest MeHg to THg ratio, suggesting that %MeHg is a better indicator for piscivory than THg alone. | |
![]() Fig 3: Butchering a subsistence harvested bearded seal (Erignathus barbatus) in the community of Barrow, Alaska. |
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Reference list
Bratton, G. R.; Flory, W.; Spainhour, C. B., and
Haubold, E. M. Assessment of selected heavy metals in liver, kidney, muscle,
blubber, and visceral fat of Eskimo harvested bowhead whales Baleana mysticetus
from Alaska's North Coast. Barrow, Alaska: Department of Wildlife Management,
North Slope Borough; 1997.
Woshner, V. M.; O'Hara, T. M.; Bratton, G. R.; Suydam, R. S., and Beasley, V. R. Concentrations and interactions of selected essential and non-essential elements in bowhead and beluga whales of Arctic Alaska. Journal of Wildlife Diseases. 2001; 37(4):693-710.

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