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Conversely, the Gippsland Lakes population may feed on the prey items sampled in addition to lower trophic level prey that will lower the average δ15N signature received.
Within the SABD it has been observed that the active foraging strategy of the Gippsland Lakes population differs from that of the Port Phillip Bay population (Dolphin Research Institute Charlton-Robbb, et al., unpublished data).
For the SABD populations, the Port Phillip Bay population displayed significantly higher δ15N (17.0‰ vs. 15.5‰) values than the Gippsland Lakes population (F1, 12 = 8.100, p = 0.015) (Figure 2).
The Port Phillip Bay population was 4.5‰ higher for δ15N than the average signature of the potential prey items, whereas the Gippsland Lakes population was only 1.3‰ higher than the same potential prey species sampled in the Gippsland Lakes.
The Port Phillip Bay population displayed a significantly higher δ15N than the Gippsland Lakes population (17.0‰ vs. 15.5‰), suggesting that the Port Phillip Bay population may feed at a higher trophic level - a result which is supported by analysis of local food chains.
Both of these population sizes are small with ongoing population studies suggesting that the southern Port Phillip Bay population is comprised of approximately 80 individuals and the Gippsland Lakes population is comprised of approximately 50 individuals (Dolphin Research Institute Charlton-Robbb, et al., unpublished data).
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Using growth factor combination 4 (Table S2), we found differences in the statistical significance of L P50 declines for Iliamna Lake populations but not for Wood River lakes populations.
The significant decreases in length at age ranged from 22 to 37 mm for Iliamna Lake populations and 62 106 mm for Wood River lakes populations.
L P50 values did depend on marine growth factors, decreasing with time for all populations and growth factor combinations by 4.7 45.4 mm for Iliamna Lake populations and 5.4 45.6 mm for Wood River lakes populations.
From the Wood River lakes populations, we estimated ocean age 2 PMRNs over 14 cohorts from 1958 1962 and 1994 2004.
Mitochondrial DNA variation approaches zero in the Sonora Pass, White Mountain and Graveyard Lakes populations (range θ S per bp = 0.000-0.001, range θ π per bp = 0.000-0.001).
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