The State of Circumpolar Walrus Populations
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Canadian High Arctic - Northwest Greenland (CHA-NWG) population are not as discrete as<br />
previously assumed (NAMMCO 2015). Additional research is needed to inform harvest<br />
management. For the Canadian Central Arctic - West Greenland (CCA-WG) population, an<br />
increased understanding <strong>of</strong> the seasonal movements between the two countries will improve<br />
inter-jurisdictional management <strong>of</strong> harvesting and other population stressors (e.g., oil and gas<br />
development). Seasonal movements within and between different areas occupied by this<br />
population (e.g., movements, if any, between Foxe Basin or South and East Hudson Bay and<br />
northwest Hudson Bay/Hudson Strait) could also be studied via tagging. <strong>The</strong> Canadian Low<br />
Arctic (CLA) population in southeast Hudson Bay is considered a separate population, but this is<br />
tentative as there are no data to confirm. Research on movement patterns <strong>of</strong> these animals (e.g.,<br />
via satellite-tagging), particularly whether they move into Hudson Strait, is needed (also see<br />
Genetics, below).<br />
For the Kara Sea - Southern Barents Sea – Novaya Zemlya (KS-SBS-NZ) population, data on the<br />
distribution <strong>of</strong> walruses during the spring breeding season and on seasonal movements are<br />
needed. <strong>The</strong> relationship <strong>of</strong> Atlantic walruses in the Svalbard – Franz Josef Land Population (S-<br />
FJL) population to those in the KS-SBS-NZ population is uncertain (Born et al. 1995; NAMMCO<br />
2006; Boltunov et al. 2010; Shitova et al. 2014b). <strong>The</strong>re is extensive oil exploration, development<br />
and production currently taking place in the Pechora Sea and southwest Kara Sea. Data on walrus<br />
distribution and movements are needed to assess the risks posed by these industrial activities to<br />
walruses and their prey.<br />
For Pacific walruses, data on Laptev Sea walrus movements and distribution are needed.<br />
Movements <strong>of</strong> animals in the Bering and Chukchi Seas (BCS) population <strong>of</strong> Pacific walruses have<br />
been extensively studied through the use <strong>of</strong> satellite-telemetry (Jay and Garner 2002; Jay and<br />
Hills 2005; Jay et al. 2006, 2010, 2012, 2014), providing critical information for assessing<br />
impacts from industrial development and climate change. Continuing this work could provide<br />
valuable early information on the direction and extent <strong>of</strong> changes in walrus distribution and<br />
abundance in response to climate change and other stressors, and thereby benefit population<br />
management. Genetic data will also assist in understanding walrus movement patterns (see<br />
below).<br />
Abundance estimates are available for most populations, but with considerable uncertainty. Bias<br />
and imprecision in estimated population sizes over time leads to uncertainty in understanding<br />
trends in absolute population size (e.g., Taylor and Udevitz 2015). Population estimates are<br />
generally negatively biased due to incomplete survey coverage and methodological issues.<br />
Research on ways to increase the precision and accuracy <strong>of</strong> survey estimates using different<br />
methods (e.g., genetic capture-mark-recapture as an potential alternative to aerial surveys) and