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Exposure to risk factors experienced during migration is not associated with recent Vermivora warbler population trends

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Context Understanding the factors limiting populations of animals is critical for effective conservation. Determining which factors limit populations of migratory species can be especially challenging because of their reliance on multiple, often geographically distant regions during their annual cycles. Objectives We investigated whether distribution-wide variation in recent breeding population trends was more strongly associated with exposure to risk factors experienced during migration (i.e., natural and anthropogenic threats often associated with increased mortality or carry-over effects) or factors associated with breeding and nonbreeding areas in golden-winged warblers (Vermivora chrysoptera) and blue-winged warblers (V. cyanoptera), two Nearctic-Neotropical migrants experiencing regionally variable population trends. Methods We used geolocator data from 85 Vermivora warblers (n = 90 geolocator tracks) tracked from North American breeding locations and Central American nonbreeding locations from 2013 to 2017 to determine variation in space use among populations. We assessed whether differences in space use among populations of Vermivora warblers during migration were associated with exposure to migration risk-factors and whether increased relative exposure to migration risk factors was associated with population declines at regional and subregional scales. Results Regional and subregional populations of Vermivora warblers exhibited variation in space use and exposure to anthropogenic and natural risk-factors. However, we found no evidence that recent variation in population trends of Vermivora warblers was associated with risk-factors experienced by different populations during migration. Instead, factors associated with land cover-types in breeding and nonbreeding areas were more strongly associated with recent population trends. Conclusions Understanding how populations of migratory birds are affected by factors experienced during migration is critical for their conservation. We did not find evidence that variation in exposure to migration risk-factors is associated with recent regional or subregional variation in Vermivora warbler population trends. Consequently, our results suggest that efforts to reverse ongoing population declines of Vermivora warblers may be more effective if directed toward conservation actions targeting limiting factors within the breeding and nonbreeding periods versus those directed at conditions encountered during migration. We caution that geographic variation in projected land-use change may differentially affect areas used by different populations of Vermivora warblers during migration, posing a potential threat to these species in the future.
A Regional population-specific core-use areas (25th percentile) of Vermivora warblers during autumn and spring migration. Blue-winged warblers and golden-winged warblers from breeding sites (triangles) associated with different Bird Conservation Regions (BCRs) are represented by different colors. Geolocator-derived nonbreeding and breeding location estimates are identified by × ’s and + ’s, respectively and colored according to breeding population (i.e., BCR). B The spatial distribution of the mean-adjusted cumulative exposure to migration risk-factors represents the sum of standardized rasters of eight migration risk-factors considered in our analyses. Red cells indicate areas with above-average exposure to migration risk-factors whereas blue cells are associated with below-average exposure. Boxplot shows the scaled exposure of different regional populations (based on the exposure of individuals tracked within each population; colors correspond with the A) of Vermivora warblers to the mean-adjusted cumulative exposure to migration risk factors. Populations that experienced different levels of exposure (based on one-way ANOVA and Tukey HSD; P < 0.05) are denoted with letters. Values inside boxes indicate regional population trend estimates from the Breeding Bird Survey (BBS) for 2000–2015 (BBS Regional Trend Analysis Form). Asterisks specify population trends with 95% confidence intervals that do not overlap zero. Regional populations are defined by BCR and species (blue-winged warbler [BW] or golden-winged warbler [GW]) in boxplot legend: Prairie Hardwood Transition BCR (BW PHT, teal), Central Hardwoods BCR (BW CH, pink), Appalachian Mountains BCR (BW AM, light orange; GW AM, dark orange), and Boreal Hardwood Transition (GW BHT; maroon) BCR
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Landsc Ecol (2023) 38:2357–2380
https://doi.org/10.1007/s10980-023-01701-2
RESEARCH ARTICLE
Exposure torisk factors experienced duringmigration
isnotassociated withrecent Vermivora warbler population
trends
GunnarR.Kramer· DavidE.Andersen· DavidA.Buehler· PetraB.Wood· SeanM.Peterson·
JustinA.Lehman· KyleR.Aldinger· LesleyP.Bulluck· SergioHarding· JohnA.Jones·
JohnP.Loegering· CurtisSmalling· RachelVallender· HenryM.Streby
Received: 25 October 2022 / Accepted: 4 June 2023 / Published online: 21 June 2023
© The Author(s), under exclusive licence to Springer Nature B.V. 2023
Abstract
Context Understanding the factors limiting popu-
lations of animals is critical for effective conserva-
tion. Determining which factors limit populations
of migratory species can be especially challenging
because of their reliance on multiple, often geograph-
ically distant regions during their annual cycles.
Objectives We investigated whether distribution-
wide variation in recent breeding population trends
was more strongly associated with exposure to risk
factors experienced during migration (i.e., natu-
ral and anthropogenic threats often associated with
increased mortality or carry-over effects) or fac-
tors associated with breeding and nonbreeding areas
in golden-winged warblers (Vermivora chrysop-
tera) and blue-winged warblers (V. cyanoptera), two
Supplementary Information The online version
contains supplementary material available at https:// doi.
org/ 10. 1007/ s10980- 023- 01701-2.
G.R.Kramer(*)· H.M.Streby
Department ofEnvironmental Sciences, University
ofToledo, Toledo, OH43606, USA
e-mail: gunnarrkramer@gmail.com
Present Address:
G.R.Kramer
Department ofOrganismic andEvolutionary Biology,
Harvard University, 26 Oxford Street, Cambridge,
MA02138, USA
D.E.Andersen
U.S. Geological Survey, Minnesota Cooperative Fish
andWildlife Research Unit, University ofMinnesota,
St.Paul, MN55108, USA
D.A.Buehler· J.A.Lehman
Department ofForestry, Wildlife andFisheries, University
ofTennessee, Knoxville, TN37996, USA
P.B.Wood
U.S. Geological Survey, West Virginia Cooperative Fish
andWildlife Research Unit, West Virginia University,
Morgantown, WV26506, USA
S.M.Peterson
Department ofEnvironmental Science, Policy,
andManagement, University ofCalifornia, Berkeley,
CA94720, USA
K.R.Aldinger
West Virginia Cooperative Fish andWildlife Research
Unit, West Virginia University, Morgantown, WV26506,
USA
L.P.Bulluck
Center forEnvironmental Studies, Virginia
Commonwealth University, Richmond, VA23284, USA
S.Harding
Virginia Department ofWildlife Resources, Henrico,
VA23228, USA
J.A.Jones
Department ofEcology andEvolutionary Biology, Tulane
University, NewOrleans, LA70118, USA
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
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