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Assessing Climate Change Vulnerability of Breeding Birds in Arctic ...

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Greater White-fronted Goose (Anser albifrons)<strong>Vulnerability</strong>: Presumed StableConfidence: ModerateThe Greater White-fronted Goose, with a nearly circumpolar distribution, has the most expansiverange <strong>of</strong> any species <strong>in</strong> its genus. In Alaska, this species breeds <strong>in</strong> large numbers <strong>in</strong> both theYukon-Kuskokwim Delta and also on the <strong>Arctic</strong> Coastal Pla<strong>in</strong>, but they will also nest <strong>in</strong> the<strong>in</strong>terior. On the coastal pla<strong>in</strong> breed<strong>in</strong>g habitat ranges from lowland wet to upland dry tundra<strong>of</strong>ten near ponds or lakes (Ely and Dzub<strong>in</strong> 1994). The Greater White-fronted Goose diet isdom<strong>in</strong>ated by vegetative matter, primarily grass and sedge rhizomes, tubers, and berries (Ely andDzub<strong>in</strong> 1994). <strong>Arctic</strong> Alaskan populations w<strong>in</strong>ter on the Gulf Coastal pla<strong>in</strong> <strong>in</strong> Louisiana andTexas as well as northern Mexico (Ely and Dzub<strong>in</strong> 1994). The Alaskan <strong>Arctic</strong> Coastal Pla<strong>in</strong>population is estimated at 200,000 and population growth has been rapid <strong>in</strong> the past decade buthas recently leveled <strong>of</strong>f (Larned et al. 2012).J. Liebezeit @ WCSRange: We used the extant NatureServe map forthe assessment as it matched other range mapsources and descriptions (Johnson and Herter1989, Ely and Dzub<strong>in</strong>1994).Physiological Hydro Niche: Among the <strong>in</strong>directexposure and sensitivity factors <strong>in</strong> theassessment (see table on next page), GreaterWhite-fronted Goose ranked neutral <strong>in</strong> mostcategories with the exception <strong>of</strong> physiologicalhydrologic niche for which they were evaluatedto have a “slightly to greatly <strong>in</strong>creased”vulnerability. This response was drivenprimarily by this species reliance on waterbodies for breed<strong>in</strong>g and forag<strong>in</strong>g. A dry<strong>in</strong>g trendcould have negative impacts by reduc<strong>in</strong>gavailability <strong>of</strong> suitable habitats. Currentprojections <strong>of</strong> annual potential evapotranspirationsuggest negligible atmosphericdrivendry<strong>in</strong>g for the foreseeable future (TWSand SNAP). Thus atmospheric moisture, as anexposure factor (most <strong>in</strong>fluential on the“hydrological niche” sensitivity category), wasnot heavily weighted <strong>in</strong> the assessment.Human Response to CC: All-weather roads(necessitated by a warm<strong>in</strong>g climate andshortened ice road season) associated withenergy extraction activities could impact GreaterWhite-fronted Geese, particularly nearTeshekpuk Lake, however other sources <strong>of</strong>human activity related to climate changemitigation will be much less pervasive <strong>in</strong> thenear future so would likely only slightly <strong>in</strong>creasevulnerability.Disturbance Regime: <strong>Climate</strong>-mediateddisturbance processes, namely thermokarst,could both create and destroy forag<strong>in</strong>g andnest<strong>in</strong>g habitats through both ice wedgedegradation and dra<strong>in</strong><strong>in</strong>g <strong>of</strong> thaw lakes (Mart<strong>in</strong>et al. 2009). Likewise, predicted <strong>in</strong>creasedcoastal erosion and result<strong>in</strong>g sal<strong>in</strong>ization (Joneset al. 2009) could both negatively and positivelyaffect post-breed<strong>in</strong>g aggregations <strong>of</strong> stag<strong>in</strong>gbirds by destroy<strong>in</strong>g and creat<strong>in</strong>g forag<strong>in</strong>g /molt<strong>in</strong>g habitat.42

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