No abstract

Despite a historically large degree of philopatry to the Gulf Coastal Plains wintering area in the United States and Mexico, the midcontinent population of greater white‐fronted geese (Anser albifrons) has demonstrated changes in their winter distribution in recent decades, warranting investigation into the timing and magnitude of change. We evaluated spatiotemporal patterns in winter band recovery distribution from 1974–2018 and midwinter waterfowl survey counts for midcontinent greater white‐fronted geese. We used an overlap similarity index to compare annual winter band recovery distributions with a historical reference distribution of 1955–1974, followed by a changepoint analysis to assess the timing and magnitude of distributional change. Our analyses revealed a 2‐stage shift in the distribution of winter band recoveries from midcontinent greater white‐fronted geese that occurred following the 1994–1995 season and the 2009–2010 season. As a result, the spatiotemporal distribution of midcontinent greater white‐fronted goose band recoveries can be explained in 3 distinct time eras: the historical era (1974–1995), the transitional era (1995–2010), and the current era (2010–2018). Patterns in midwinter waterfowl survey counts were consistent with changes in winter band recovery distributions, providing further support that midcontinent greater white‐fronted geese have shifted their core winter distribution nearly 750 km northeast over the last 5 decades from the Gulf Coastal Plain to the Mississippi Alluvial Valley. Quantifying the timing and magnitude of this shift in winter distribution of midcontinent greater white‐fronted geese provides clarity to previous patterns in and changes to harvest distribution and could be used to facilitate future decisions regarding harvest management, regulatory frameworks, and habitat conservation planning efforts.

Numbers of temperate-breeding Atlantic and Mississippi Flyway Canada geese have greatly increased since the 1980s. Consequently, numbers of yearlings, sub-adults and failed breeders undertaking pre-molt migration to northern latitudes has also increased, potentially providing additional hunting opportunities for Cree hunters living near James Bay, Canada. We described movement patterns and habitat use of molt migrant Canada geese Brenta canadensis maxima along the east coast of James Bay based on nine geese fitted with GSM-GPS devices during 11 northward and eight southward migrations between 2015 and 2019. Geese staged for 2.8 ± 0.6 days (mean ± standard error of the mean) at 3.2 ± 0.6 staging sites (mostly tidal flats and salt marshes) from the first week of June in spring and 3.8 ± 1.8 days at 2.0 ± 0.5 staging sites (mostly inland freshwater wetlands, peatlands and tidal flats) from the first week of September when returning south. Shallow and deep water habitats were used as resting sites during both migrations. In spring, molt migrants were mostly harvested in June well after the migration of sub-arctic breeding geese whereas in autumn, both subspecies were harvested in September. Molt migrant temperate-breeding geese can increase harvest opportunities and represent supplementary wildlife food for Cree communities. However, the current number of molt migrant geese harvested by Cree hunters is not sufficient to significantly impact populations of temperate-breeding geese.

Wildlife harassment (i.e., intentional disturbance by humans) is a common nonlethal management approach employed to reduce human-wildlife conflicts, but effectiveness is often undocumented or uncertain. We evaluated the effect of harassment on Canada goose (Branta canadensis) behavior in an urban area during winter. Winter can be a challenging period for waterfowl given limited food availability and greater thermoregulatory costs; thus, we expected that harassment in winter may be more effective than during other portions of