The marine ecosystem around the Antarctic Peninsula is experiencing dramatic warming (Vaughn et al. 2003) and significant reductions in the extent and duration of seasonal sea ice cover (Stammerjohn et al. 2008). These changes affect every component of the ecosystem (Schofield et al. 2010, Ducklow et al. 2012), but particularly the demography and ecology of Antarctic krill (Euphausia superba) and the predators that rely on krill as their primary prey. The life history and population dynamics of krill are heavily influenced by climate forcing (Nicol 2006), thus krill predators must respond to both seasonal and inter-annual variability in prey availability and alter their behavior and demography in response to such changes (e.g. penguins and seals; Fraser et al. 1992, Reid and Croxall 2001, Fraser and Hofmann 2003, Reid et al. 2005).
The largest krill predators found in the nearshore waters around the Antarctic Peninsula are humpback whales (Megaptera novaeangliae). Since the cessation of commercial whaling, these whales have recovered quickly and are now the most numerous baleen whale species in the region. Previous work by our group has shown that the broad-scale distribution patterns of these whales is mostly related to areas with increased krill abundance (Friedlaender et al. 2006, 2011), and that seasonal movement patterns of the whales seem to be linked with offshore to onshore movement patterns of krill from summer to fall (Figure 2, Curtice et al. 2015). More recent work is providing greater insights regarding how the density (Figure 3, Johnston et al. in review) and foraging behavior (Friedlaender et al. 2013, accepted) of these whales reflects the broad-scale distribution of resources and environmental conditions around the Antarctic Peninsula.
Because of their enormous size, humpback whales have high energetic demands that can only be met by foraging on high-density prey patches (e.g. Goldbogen et al. 2010). As a result, humpback whales distribute themselves and move between areas of increased prey abundance throughout the Antarctic feeding season. Antarctic krill predators that are tied to land or sea ice as a substrate to provision young and rest (e.g. penguins and seals) are susceptible to local changes in the availability of prey. Seasonal changes in krill availability can therefore have significant consequences on the survival of these central-place foragers. Baleen whales, however, are more mobile and able to find prey across a much broader spatial and temporal scale. However, because of their increased energetic demands relative to smaller animals, whales require high densities of krill. Much like commercial fishing is more efficient in areas with high densities of targeted resources, baleen whales seek areas of high krill availability (e.g. Nowacek et al. 2011, Johnston et al. 2012). It is therefore imperative to understand the areas in which whales forage and how these areas overlap with existing fishing grounds (in both space and time) so that proper management and conservation strategies can be implemented.