Mark Hebblewhite’s research while affiliated with University of Montana and other places

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Publications (314)


Map of study area showing Banff, Kootenay, and Yoho National Parks and the Ya Ha Tinda region within British Columbia and Alberta, Canada. Colored points represent the average number of grizzly bear detections per month at 625 remote camera locations from 2012 to 2023. Stars represent towns, and white lines represent paved roads. The TransCanada Highway and parallel railway run through the center of the study area from Canmore, Alberta, through Golden, British Columbia.
Violin plots from a simulation study assessing the effects of abundance (N = 60 and 120), home range size, detection rates, and number of marked animals on one‐ and two‐stage generalized spatial mark–resight (gSMR) abundance estimates. Violin plots show the distribution of posterior median values from 200 simulations per scenario. Red dashed lines indicate true values.
Simulation study results showing root mean squared error (RMSE) of abundance estimates as a function of abundance (N = 60 and 120), home range size, detection rates, and number of marked animals for one‐ and two‐stage generalized spatial mark–resight (gSMR) models.
Number of remote camera sites, detections of unmarked grizzly bears, detections of reproductive females, number of marked animals, and number of marked detections by year within the Banff, Kootenay, Yoho, and Ya Ha Tinda study area. The bottom right panels show a radio‐collared grizzly bear detected at a rub tree and a second unmarked grizzly bear at a high‐elevation remote camera site. Photo credit: Parks Canada.
Realized trends of grizzly bear density (number per 1000 km²) with 95% Bayesian credible intervals from 2012 to 2023. The population of grizzly bears increased across the study area but decreased within 4 km of paved roads and increased far from paved roads. The density of reproductive females was lower than the population of grizzly bears and increased with time.

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One‐stage spatial mark–resight analysis reveals an increasing grizzly bear population with declining density near roads
  • Article
  • Full-text available

April 2025

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57 Reads

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Mark Hebblewhite

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Connor Meyer

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[...]

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Seth G. Cherry

Wildlife ecologists throughout the world strive to monitor trends in population abundance to help manage wildlife populations and conserve species at risk. Spatial capture–recapture studies are the gold standard for monitoring density, yet they can be difficult to apply because researchers must be able to distinguish all detected individuals. Spatial mark–resight (SMR) models only require a subset of the population to be marked and identifiable. Recent advances in SMR models with radio‐collared animals required a two‐staged analysis. We developed a one‐stage generalized SMR (gSMR) model that used detection histories of marked and unmarked animals in a single analysis. We used simulations to assess the performance of one‐ and two‐stage gSMR models. We then applied the one‐stage gSMR with telemetry and remote camera data to estimate grizzly bear (Ursus arctos) abundance from 2012 to 2023 within the Canadian Rocky Mountains. We estimated abundance trends for the population and reproductive females (females with cubs of the year). Simulations suggest that one‐ and two‐stage models performed equally well. One‐stage models are more dependable as they use exact likelihoods, whereas two‐stage models have shorter computation times for large data sets. Both methods had >95% credible interval coverage and minimal bias. Increasing the number of marked animals increased the accuracy and precision of abundance estimates, and ≥10 marked animals were required to obtain coefficients of variation <20% in most scenarios. The grizzly bear population increased slightly (growth rate λmean = 1.02) to a 2023 density of 10.4 grizzly bears/1000 km². Reproductive female abundance had high interannual variability and increased to 1.0 bears/1000 km². Population density was highest within protected areas, within high‐quality habitat and far from paved roads. The density of activity centers declined near paved roads over time. Mechanisms of decline may have included direct mortality and shifting activity centers to avoid human activity. Our study demonstrates the influence of human activity on localized density and the importance of protected areas for carnivore conservation. Finally, our study highlights the widespread utility of remote camera and telemetry‐based SMR models for monitoring spatiotemporal trends in abundance.

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SNAPSHOT USA 2019-2023: The First Five Years of Data From a Coordinated Camera Trap Survey of the United States

January 2025

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896 Reads

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3 Citations

Global Ecology and Biogeography

Motivation: SNAPSHOT USA is an annual, multicontributor camera trap survey of mammals across the United States. The growing SNAPSHOT USA dataset is intended for tracking the spatial and temporal responses of mammal populations to changes in land use, land cover and climate. These data will be useful for exploring the drivers of spatial and temporal changes in relative abundance and distribution, as well as the impacts of species interactions on daily activity patterns. Main Types of Variables Contained: SNAPSHOT USA 2019–2023 contains 987,979 records of camera trap image sequence data and 9694 records of camera trap deployment metadata. Spatial Location and Grain: Data were collected across the United States of America in all 50 states, 12 ecoregions and many ecosystems. Time Period and Grain: Data were collected between 1st August and 29th December each year from 2019 to 2023. Major Taxa and Level of Measurement: The dataset includes a wide range of taxa but is primarily focused on medium to large mammals. Software Format: SNAPSHOT USA 2019–2023 comprises two .csv files. The original data can be found within the SNAPSHOT USA Initiative in the Wildlife Insights platform.


FIGURE 1 | (a) The median centres of all 263 SNAPSHOT USA 2019-2023 camera trap arrays overlaying a simplified derivation of Bailey's ecoregions (Bailey 2016) in the United States; ecoregions currently represented by SNAPSHOT USA are in colour, while ecoregions that lack surveys are in grey. (b) Number of arrays per 100,000 km 2 (*ecoregions under 100,000 km 2 ).
FIGURE 2 | (a) Map of the United States showing all 263 SNAPSHOT USA 2019-2023 camera trap arrays, with their colour and size representing the number of years the array was surveyed. (b) The same map showing all the arrays, with colour representing the maximum number of identified mammal and large ground bird species in a single survey year and size representing the number of detections of those species per 100 camera trap-nights observed within the array that year. Only detections of mammals and large ground birds (wild turkey (Meleagris gallopavo), grouse (Canachites spp., Bonasa spp., Tympanuchus spp., Dendragapus spp., Centrocercus spp.) or quail (Callipepla spp., Oreortyx spp.)) identified to species level were used to obtain these values, and each detection represents one sequence of images captured by a camera.
Variable information for sequence data from SNAPSHOT USA 2019-2023.
Variable information for deployment data from SNAPSHOT USA 2019-2023.
Global Ecology and Biogeography SNAPSHOT USA 2019-2023: The First Five Years of Data From a Coordinated Camera Trap Survey of the United States

January 2025

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244 Reads

Global Ecology and Biogeography

Motivation: SNAPSHOT USA is an annual, multicontributor camera trap survey of mammals across the United States. The growing SNAPSHOT USA dataset is intended for tracking the spatial and temporal responses of mammal populations to changes in land use, land cover and climate. These data will be useful for exploring the drivers of spatial and temporal changes in relative abundance and distribution, as well as the impacts of species interactions on daily activity patterns. Main Types of Variables Contained: SNAPSHOT USA 2019-2023 contains 987,979 records of camera trap image sequence data and 9694 records of camera trap deployment metadata. Spatial Location and Grain: Data were collected across the United States of America in all 50 states, 12 ecoregions and many ecosystems. Time Period and Grain: Data were collected between 1st August and 29th December each year from 2019 to 2023. Major Taxa and Level of Measurement: The dataset includes a wide range of taxa but is primarily focused on medium to large mammals. Software Format: SNAPSHOT USA 2019-2023 comprises two .csv files. The original data can be found within the SNAPSHOT USA Initiative in the Wildlife Insights platform.


Map of the Sikhote‐Alin Biosphere Zapovednik and adjacent Terney Hunting Lease in central Sikhote‐Alin, Russian Far East. Snow track surveys were conducted and random cameras deployed in the 3.5 × 3.5 km grid in the southern portion of SABZ. Elevation bins were chosen to illustrate main ridges of the Sikhote‐Alin mountains. Cameras deployed during winter 2021–2022 are shown as example locations.
Relationship between estimates of population density from random FMP track surveys (x‐axis) and other methods (y‐axis). Error bars represent 95% confidence intervals. The solid line indicates a 1:1 correlation between mean estimates, while dotted lines represent the actual estimated relationship between the mean density of the two models. Estimates are shown from early spring 2020 (February 01, 2020 to March 26, 2020) and winter 2021–2022 (December 01, 2021 to February 01, 2022), as we were not able to conduct random snow tracking surveys in winter 2020–2021 due to COVID‐19. The two colors represent the two approaches to data collection: snow track surveys and camera traps. Each species is represented by a different shape at the point estimate. Please note the pseudo‐log scale of the y‐axis.
Total prey biomass (kg/km²) over 3 years (2020–2022) in southern Sikhote‐Alin Zapovednik, Russian Far East. Total biomass was estimated by multiplying point estimates of species densities by average female weights reported in the literature (Bromley and Kucherenko 1983), then taking their sum. We note that African swine fever arrived in our study area between our first and second years of sampling, causing a large decrease in wild boar density and, therefore, biomass.
Cameras or Camus? Comparing Snow Track Surveys and Camera Traps to Estimate Densities of Unmarked Wildlife Populations

December 2024

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369 Reads

Population density is a valuable metric used to manage wildlife populations. In the Russian Far East, managers use the Formozov‐ Malyushev‐Pereleshin (FMP) snow tracking method to estimate densities of ungulates for hunting management. The FMP also informs Amur tiger (Panthera tigris altaica) conservation since estimates of prey density and biomass help inform conservation interventions. Yet, climate change and challenges with survey design call into question the reliability of the FMP. Camera traps offer a promising alternative, but they remain unexplored for monitoring tiger prey density. Over three years (2020‐2022), we used the FMP and camera‐based methods to estimate densities of four prey species of the Amur tiger in the Sikhote‐ Alin Biosphere Reserve, Russian Far East: wild boar (Sus scrofa), red deer (Cervus canadensis), roe deer (Capreolus pygargus), and sika deer (Cervus nippon). We compared FMP results from snow track survey routes either along trails, or along routes representative of the study area, and estimates derived from camera data using the random encounter model (REM), space‐to‐event model (STE), and time‐to‐event model (TTE). We found that density estimates from representative routes were typically lower than routes along trails and indicated different relative densities of prey. Density estimates from camera traps and representative track surveys were generally similar with no significant relative bias, but precision was poor for all methods. Differences between estimates were amplified when converted to prey biomass, particularly with larger, more abundant prey, which poses a challenge for their utility for tiger managers. We conclude camera traps can offer an alternative to snow track surveys when monitoring unmarked prey, but we caution that they require considerably more resources to implement. Tiger managers should be especially cautious when extrapolating density to estimates of prey biomass, and we encourage future research to develop more robust methods for doing so.


Distribution and sample sizes of social pairs of six Canis species around the world used to investigate factors influencing cohesion and home range overlap within canid social groups, 2003–2019.
Boxplots showing (a) cohesion and (b) home range overlap between social pairs of canids, 2003–2019, estimated from telemetry data. Black lines in boxes are median values, boxes are bounded by the 25th and 75th percentiles (interquartile range), error bars include the largest values within 1.5 × the interquartile range, black circles are values outside of 1.5 × the interquartile range, and green circles are all data values. Sample sizes are season–pair combinations.
Cohesion of social pairs of wolves and coyotes during winter and pup‐rearing. Pairs are separated as breeding pairs and pairs containing at least one nonbreeder (other pairs). Black lines in boxes are median values, boxes are bounded by the interquartile range, error bars include the largest values within 1.5× the interquartile range, and red circles are all data values. Sample sizes are season‐pair combinations.
Relationships between cohesion of social wolf pairs and (a) variation in precipitation (CV), (b) anthropogenic landscape modification, and (c) group size across their geographic distribution in winter and pup‐rearing seasons as estimated with generalized additive mixed models.
Intrinsic and environmental drivers of pairwise cohesion in wild Canis social groups

December 2024

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986 Reads

Animals within social groups respond to costs and benefits of sociality by adjusting the proportion of time they spend in close proximity to other individuals in the group (cohesion). Variation in cohesion between individuals, in turn, shapes important group‐level processes such as subgroup formation and fission–fusion dynamics. Although critical to animal sociality, a comprehensive understanding of the factors influencing cohesion remains a gap in our knowledge of cooperative behavior in animals. We tracked 574 individuals from six species within the genus Canis in 15 countries on four continents with GPS telemetry to estimate the time that pairs of individuals within social groups spent in close proximity and test hypotheses regarding drivers of cohesion. Pairs of social canids (Canis spp.) varied widely in the proportion of time they spent together (5%–100%) during seasonal monitoring periods relative to both intrinsic characteristics and environmental conditions. The majority of our data came from three species of wolves (gray wolves, eastern wolves, and red wolves) and coyotes. For these species, cohesion within social groups was greatest between breeding pairs and varied seasonally as the nature of cooperative activities changed relative to annual life history patterns. Across species, wolves were more cohesive than coyotes. For wolves, pairs were less cohesive in larger groups, and when suitable, small prey was present reflecting the constraints of food resources and intragroup competition on social associations. Pair cohesion in wolves declined with increased anthropogenic modification of the landscape and greater climatic variability, underscoring challenges for conserving social top predators in a changing world. We show that pairwise cohesion in social groups varies strongly both within and across Canis species, as individuals respond to changing ecological context defined by resources, competition, and anthropogenic disturbance. Our work highlights that cohesion is a highly plastic component of animal sociality that holds significant promise for elucidating ecological and evolutionary mechanisms underlying cooperative behavior.


Conceptual framework and analytical steps for studying the interplay of neonatal tactics (hider versus follower offspring) and environmental context (resource productivity and spatial scale of resource variation⁸) on residency level, movement metrics and the resulting home range of females before and after giving birth
Step 1 classifies female movement as fitting a Brownian or an Ornstein–Uhlenbeck (OU) type of movement model (see Methods and glossary in Table 1). A female is defined as ‘resident’ if her movement is best described by an OU model. The figure in the step 1 panel displays how the proportion of residents in a population is expected to vary pre- and post-birth in species with hider and follower offspring, across gradients of resource productivity or spatial scale of resource variation. Step 2 corresponds to the predictions for how the two movement metrics (diffusion in orange and return rate in purple) and the resulting home range size (in black) should respond pre- and post-birth to the same environmental variables depending on neonatal tactics. Note that, when a movement is best described by a Brownian model (no ‘residency’), only diffusion (hence, neither return rate nor home range size) can be estimated.
Overview of the species and populations
a, The phylogenetic tree of the 23 species of large herbivores included in this study (see ‘Phylogenetic analysis’ section in Supplementary Table 2). The number of populations for each species is indicated on each pictogram (downloaded from http://www.phylopic.org or from the personal collection of the authors). Blue and red represent follower and hider neonatal antipredator strategies, respectively. b, The average location of each population (Supplementary Table 1) on a composite map of cumulative Normalized Difference Vegetation Index (NDVI) values, retrieved from ref. ⁷⁶ and used solely for presentation purposes. Credit: a, Silhouettes adapted from PhyloPic under a Creative Commons license.
Changes in ranging behaviour of females before and after parturition according to the antipredator strategy of their offspring, and the mean quantity and spatial distribution of food resources
a,b, Changes in the propensity for a female to be resident across populations of 23 species of large herbivores in the pre-parturition period (a) and in the post-parturition period (b), in relation to increasing spatial scale of resource variation (measured by SSNDVI) with follower (in blue) and hider (in red) offspring. Points, lines and shading represent mean probability, model fit and its associated 95% credible intervals, respectively. The point size is proportional to the number of females.
Changes in two movement components (diffusion and frequency of return rates) of females before and after parturition according to the antipredator strategy of their offspring, and the mean quantity and spatial distribution of food resources
a–d, Changes in expected values of diffusion (a and b) and return rates (c and d) for females across 23 species of large herbivores in relation to mean resource productivity (a and c, measured by mean NDVI) and spatial scale of resource variation (b and d, measured by SSNDVI) before (dark shading) and following (light shading) parturition with hider (red roe deer fawn) and follower (blue chamois kid) offspring. Low, mean and high categories represent the 10%, mean and 90% quantiles of each environmental variable. e, A histogram showing the repeatability of diffusion and return rates, two components of continuous time stochastic movement models (CTMMs), according to the different levels of observation (individual, population and species) and time in years.
Contribution of two movement components (diffusion and frequency of return rates) on the change in home range size of females before and after parturition according to the antipredator strategy of their offspring, and the mean quantity and spatial distribution of food resources
a,b, Expected mean values of diffusion and return rates of adult females across populations of 23 species of large terrestrial herbivores in relation to mean resource productivity (measured as mean NDVI) (a) and spatial scale of resource variation (measured by SSNDV I) (b) before (start of arrow) and following (arrow tip) parturition with hider (in red with a deer fawn symbol) and follower (in blue with a chamois kid symbol) offspring. ‘Low’, ’mean’ and ’high’ represent the 10%, 50% and 90% quantiles of each environmental factor (0.18, 0.41 and 0.72 for mean NDVI, and 0.25, 1.33 and 6.5 km for SSNDV I), respectively. Home range size (horizontal dotted grey lines) increases with increasing diffusion and decreasing return rate, the two components of continuous time stochastic movement models (CTMMs).
Neonatal antipredator tactics shape female movement patterns in large herbivores

December 2024

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881 Reads

Nature Ecology & Evolution

Caring for newborn offspring hampers resource acquisition of mammalian females, curbing their ability to meet the high energy expenditure of early lactation. Newborns are particularly vulnerable, and, among the large herbivores, ungulates have evolved a continuum of neonatal antipredator tactics, ranging from immobile hider (such as roe deer fawns or impala calves) to highly mobile follower offspring (such as reindeer calves or chamois kids). How these tactics constrain female movements around parturition is unknown, particularly within the current context of increasing habitat fragmentation and earlier plant phenology caused by global warming. Here, using a comparative analysis across 54 populations of 23 species of large herbivores from 5 ungulate families (Bovidae, Cervidae, Equidae, Antilocapridae and Giraffidae), we show that mothers adjust their movements to variation in resource productivity and heterogeneity according to their offspring’s neonatal tactic. Mothers with hider offspring are unable to exploit environments where the variability of resources occurs at a broad scale, which might alter resource allocation compared with mothers with follower offspring. Our findings reveal that the overlooked neonatal tactic plays a key role for predicting how species are coping with environmental variation.


Yellowstone National Park, Montana wolf management units (WMU's), and all mortality locations of grey wolves (Canis lupus) collected from 1995 to 2022 in and around Yellowstone National Park, USA. Other causes of wolf mortality include, but are not limited to, interspecific conflicts, unknown natural mortality and vehicle strikes. Note that exact wolf harvest locations outside Yellowstone National Park in Wyoming are not known.
Cumulative probability of annual (September 1–August 31) survival of grey wolf (Canis lupus) survival for wolves in and around Yellowstone National Park, USA from 1995 to 2022.
Cumulative incidence function (CIF) estimates for different causes of mortality for grey wolves (Canis lupus) in and around Yellowstone National Park from 1995 to 2022 (n = 177) split by different levels of harvest intensity.
Relationships between (a) harvest mortality and annual wolf survival with uncorrected slope as the solid line and the corrected slope as the dashed line (βuncorrected = −0.78, βcorrected = −0.93, p = 0.028) and (b) harvest mortality and natural mortality (β = 0.38, p = 0.272). On panel (a) a slope of negative one indicates fully additive mortality (red dot‐dash line) and zero indicates fully compensatory mortality (dotted line). On panel (b) a slope of zero indicates fully additive mortality, and negative one indicates fully compensatory mortality. Natural mortality includes mortality from disease, malnutrition, interspecific, intraspecific and other natural causes.
Harvest of transboundary grey wolves from Yellowstone National Park is largely additive

July 2024

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286 Reads

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1 Citation

Large carnivores are globally threatened due to habitat fragmentation and loss, prey depletion and human exploitation. Human exploitation includes both legal and illegal hunting and trapping. Protected areas can create refugia from hunting and trapping; however, hunting can still threaten wide‐ranging large carnivores when they leave these areas. Large carnivore reintroductions to protected areas are often motivated to restore ecological processes, including wolf reintroduction to Yellowstone National Park (YNP). Determining if harvest is compensatory or additive is essential for informed conservation strategies, as it influences the overall impact on wolf populations and their ecosystems. If harvest was compensatory, then increasing harvest pressure outside YNP should not decrease overall survival for transboundary wolves. Alternatively, if increasing harvest was additive, then increasing harvest pressure outside YNP should decrease overall survival for transboundary wolves. We tested the effects of variable harvest pressure following delisting on the survival of YNP grey wolves (Canis lupus) from 1995 to 2022. We defined three harvest levels: no harvest, harvest with limited quotas and unlimited harvest. We used Cox‐proportional hazards models and cumulative incidence functions to estimate survival rates, factors affecting survival and cause‐specific mortality between these three harvest periods to test predictions of the additive mortality hypothesis. Most harvested wolves that primarily lived in YNP were killed adjacent to the park border. Cox‐proportional hazards models revealed that mortality was highest during years of unlimited harvest during winter outside YNP. Cause‐specific mortality analyses showed that natural mortality from other wolves and harvest were the two leading causes of death, but that harvest mortality had additive effects on wolf mortality. Wolf survival decreased with increased harvest mortality, while natural mortality remained relatively unchanged. Synthesis and applications. High rates of additive harvest mortality of wolves could negatively impact wolf survival in YNP. Harvest mortality of transboundary wolves is additive possibly due to source‐sink dynamics of uneven spatial susceptibility of wolves to harvest mortality across protected area borders, as well as effects of harvest on complex social dynamics of wolves in YNP. Transboundary management of large carnivores is challenging, yet cooperation between agencies is vital for wolf management in and around YNP. Our results support the use of small quota zones surrounding protected areas, that minimize transboundary mortality impacts on large carnivores living primarily inside protected areas.


Table 1 ).
Study area for the Fortymile Caribou Herd (FMCH; Rangifer tarandus granti) across Alaska, the United States and Yukon, Canada during summer (May 15–Aug 15) 2018–2019. Relative space use intensities of caribou (a) were estimated as a Brownian Bridge occurrence distribution using annual GPS collar locations for 47 adult females in 2018 (n = 67,662; Table S11). Video camera collar locations (n = 30 females; b) classifying behaviour as eating (green circles; n = 5549) or not eating (orange circles; n = 12,585) are overlaid onto the occurrence distribution for visual comparison.
Schematic representation of the nested, conditional discrete choices made by female caribou fitted with GPS video‐camera collars (n = 30) across (i) the six observed behaviour categories and (ii) the subsequent conditional discrete choices made among six observed categories of preferred foraging (i.e. food) categories for the Fortymile Caribou Herd, Alaska and Yukon. Conditioned on the caribou being in a particular location (All GPS Video Camera Locations), the dominant behaviour choice was classified and compared to the reference category of rumination. Then, for the subset of foraging choices, we estimated the conditional probability of caribou consuming a particular food group compared to the reference category of ground‐level vegetation. Nested probabilities are multiplicative. For example, if the probability of caribou eating (behaviour choice) is 0.5 and the probability of caribou eating lichen (food choice) is 0.5, then the probability of eating lichen is 0.5 × 0.5 = 0.25.
The predicted probability of caribou eating (behaviour) as a function of lichen and Salix spp. shrub cover relative to the reference category of ruminating for 30 adult female caribou in the Fortymile Caribou Herd (FMCH), Alaska, the United States and Yukon, Canada. We calculated the predicted probability of eating to plot the effect of each covariate on the behaviour of eating while holding the effects of other covariates at their mean. K‐folds cross validation (as a measure of goodness of fit) for the eating model was high (rs = 0.61).
Functional response curves representing the probability of eating different food types for 30 adult female caribou from the Fortymile Caribou Herd (FMCH) in Alaska, the United States and Yukon, Canada during the summers of 2018 & 2019. Probabilities of eating food type, conditioned on being in the behaviour state of eating, are displayed as a function of that food's availability on the landscape (a) and relative space use intensity of caribou derived from GPS collar locations (b). FMCH relative space use intensity represents either current year (shrubs & graminoids) or cumulative space use intensity (lichen & forbs) specific to each food choice as detailed in Table 1.
A taste of space: Remote animal observations and discrete‐choice models provide new insights into foraging and density dynamics for a large subarctic herbivore

May 2024

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290 Reads

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1 Citation

Competition for resources and space can drive forage selection of large herbivores from the bite through the landscape scale. Animal behaviour and foraging patterns are also influenced by abiotic and biotic factors. Fine‐scale mechanisms of density‐dependent foraging at the bite scale are likely consistent with density‐dependent behavioural patterns observed at broader scales, but few studies have directly tested this assertion. Here, we tested if space use intensity, a proxy of spatiotemporal density, affects foraging mechanisms at fine spatial scales similarly to density‐dependent effects observed at broader scales in caribou. We specifically assessed how behavioural choices are affected by space use intensity and environmental processes using behavioural state and forage selection data from caribou (Rangifer tarandus granti) observed from GPS video‐camera collars using a multivariate discrete‐choice modelling framework. We found that the probability of eating shrubs increased with increasing caribou space use intensity and cover of Salix spp. shrubs, whereas the probability of eating lichen decreased. Insects also affected fine‐scale foraging behaviour by reducing the overall probability of eating. Strong eastward winds mitigated negative effects of insects and resulted in higher probabilities of eating lichen. At last, caribou exhibited foraging functional responses wherein their probability of selecting each food type increased as the availability (% cover) of that food increased. Space use intensity signals of fine‐scale foraging were consistent with density‐dependent responses observed at larger scales and with recent evidence suggesting declining reproductive rates in the same caribou population. Our results highlight potential risks of overgrazing on sensitive forage species such as lichen. Remote investigation of the functional responses of foraging behaviours provides exciting future applications where spatial models can identify high‐quality habitats for conservation.


Map of our study area in the Sikhote‐Alin Biosphere Zapovednik, Russian Far East. The distribution of oak and pine forests is shown in brown and green. Average daily locations of wild boar in fall 2019 (n = 2) and fall 2020 (n = 5) are shown by yellow circles and red diamonds. The straight‐line paths between daily locations (averaged x–y coordinates) of each individual are shown with colored, dashed lines. Areas of concentrated use, where we analyzed resource selection, are shown as black crosses.
Changes in the proportion of cover type as wild boar traveled during fall 2020 and their relation to areas of concentrated use. The colors in the legend represent the different cover types. The grey sections (‘out') indicate when locations fell outside of the Zapovednik and thus lacked information on cover type. Black lines indicate the duration of successive stopover sites for each individual. The x‐axis represents the number of days since the start of each wild boar's concentrated use behavior. See the Methods section for more details on how we defined and identified these areas.
Maximum displacement of wild boar in the Sikhote‐Alin Biosphere Zapovednik, Russian Far East, during the fall 2019 and fall 2020 over periods of 1–7 days. The different quantiles of displacement values are shown by line type. Shotin et al. (2022) found wild boar infected with African Swine Fever virus did not exhibit symptoms during the first three days after infection, and these displacements are shown in green. Four days since infection was the earliest wild boar showed symptoms, while 7 days since infection was the latest, and so displacement over these periods of time are shown in orange. Displacement values were calculated over 1–7 days for each successive day of available data from each individual wild boar.
Resource‐driven changes in wild boar movement and their consequences for the spread of African Swine Fever in the Russian Far East

May 2024

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186 Reads

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1 Citation

Knowledge of animal movement patterns is invaluable to understanding the spread of diseases among wildlife populations. One example is the recent African swine fever (ASF) outbreak among wild boar Sus scrofa populations across East Asia, where there is a lack of information on movements of this species. During a wild boar tracking project to inform abundance estimation methods in the Russian Far East's Sikhote‐Alin Biosphere Zapovednik, the combination of high variability in pulsed resources of acorns and pine nuts between fall 2019 and fall 2020, and the outbreak of ASF during the latter year, offered the unique opportunity to investigate the relationship between wild boar movements to exploit pulsed resources and the potential for disease spread. We analyzed relocation data from GPS‐collared wild boar in fall 2019 and 2020 and compared them to reference data in Belgium, representative of western Europe. We found remarkable differences in movement patterns, with Far East wild boar travelling large distances in fall 2020 (maximum observed of 77 km in four days) when the availability of acorns was low. In our resource selection analysis, we found clear selection for mast‐producing forest types that corresponded with the species of greater mast production (oak or pine) for that year. Comparing the displacement of individual wild boar along a moving window of 1–7 days (time between infection and the onset ASF symptoms) highlighted the potential of rapid ASF spread over long distances when wild boar are in search of pulsed resources. This work demonstrates the capacity of wild boar to move long distances to exploit resources and emphasizes the need to consider resource availability when predicting the speed and extent to which diseases such as ASF can spread.


(a) Map of southern mountain caribou subpopulations in British Columbia and Alberta, Canada. Numbers for each subpopulation correspond to subpopulation identification numbers in Figure 2 and are numbered by Environment and Climate Change Canada (ECCC) recovery ecotype. Northern Group: 1–9, Central Group: 10–22, Southern Group: 23–41. Population growth trend for each subpopulation during the decade preceding recovery actions implementation (declining: r < −0.01, stable: r > −0.01 and r < 0.01, and increasing: r > 0.01) shown as choropleth. Because population growth estimates for individual subpopulations in (a) is based on the 10 years prior to recovery actions, it therefore does not necessarily reflect long‐term or current population trends. Refer to Figure 2 for overall population trends for each subpopulation. Functionally extirpated subpopulations are outlined in red (<10 adult females or total population <20). (b) Overall southern mountain caribou population trend from 1991 to 2023. An observed (modeled) trajectory under the recovery actions implemented is shown in green as well as a counterfactual where no recovery actions were implemented (status quo) in orange. The number of subpopulations receiving recovery actions are shown along the bottom of the plot, with values for every second year shown. The number of subpopulations with demographic data (at least one of the following: abundance, recruitment, or survival) are shown along the top of the plot, with values for every second year shown. We display this restricted (>1990) temporal span instead of the full period (1973–2023) because relatively few subpopulations have demographic data before 1990, compared to after 1990, so predictions in these earlier periods heavily rely on information from prior distributions for most subpopulations. Demographic data were available for at least half (>20) the subpopulations by 1990, so we chose this more data‐rich period as the beginning of our time frame to display the overall population trajectory. The timing of each documented subpopulation functional extirpation is shown as points along the trend. While 15 subpopulations are known to have been functionally extirpated between 1973 and 2023, three are not shown here because they occurred between 1973 and 1990, and one, Scott West, is not shown due to uncertain timing.
Median posterior estimates of abundance for each southern mountain caribou subpopulation from the integrated population model shown as orange line with 90% credible interval displayed as orange band. Extirpated and functionally extirpated subpopulations (<10 adult females or total population <20) highlighted in red. Observed minimum counts and abundance estimates shown as black dots with 90% CIs. Rug plots at top show years with survival, recruitment, or abundance data. Posterior estimates for years without demographic data rely on prior distributions as well as past and future population size. Posterior estimates before initiation of demographic data collection for each subpopulation should be interpreted cautiously. Percentage habitat loss (500 m buffered human‐caused habitat loss [Environment and Climate Change Canada, 2022b]) shown by numerical labels for each subpopulation. Individual plots for each subpopulation can be found in Lamb (2024) under CaribouIPM?BCAB/plots/by_herd/with_treatments.
Posterior distribution of estimated annual instantaneous rate of increase (r) from integrated population model for each southern mountain caribou recovery action or combination of actions. Reference condition was estimated from herd‐years when no recovery actions were applied. Rug plots along the bottom of the distributions show the average growth rate for each subpopulation the recovery action was applied to.
Posterior distributions of change in annual vital rates (after recovery action minus before) from the integrated population model for each southern mountain caribou recovery action. Rug plots along the bottom of the distributions show the average change in the rate for each subpopulation the recovery action was applied to.
(a) Effectiveness of individual southern mountain caribou recovery actions at standard application intensity assessed via generalized linear models and (b) simulated outcomes of each recovery action compared to a status quo (no recovery action) scenario. Only wolf and moose reductions were applied in isolation across multiple subpopulations and years. The remainder of the estimates is primarily derived from partitioning the individual treatment effect from a combination of actions applied concurrently and assuming effects were additive. Note that combinations of recovery actions achieve greater abundances than the sum of individual effects due to the effects of exponential growth, so small increases in population growth can yield large returns in abundance over the long term.
Effectiveness of population‐based recovery actions for threatened southern mountain caribou

April 2024

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7 Citations

Habitat loss is affecting many species, including the southern mountain caribou (Rangifer tarandus caribou) population in western North America. Over the last half century, this threatened caribou population's range and abundance have dramatically contracted. An integrated population model was used to analyze 51 years (1973–2023) of demographic data from 40 southern mountain caribou subpopulations to assess the effectiveness of population‐based recovery actions at increasing population growth. Reducing potential limiting factors on threatened caribou populations offered a rare opportunity to identify the causes of decline and assess methods of recovery. Southern mountain caribou abundance declined by 51% between 1991 and 2023, and 37% of subpopulations were functionally extirpated. Wolf reduction was the only recovery action that consistently increased population growth when applied in isolation, and combinations of wolf reductions with maternal penning or supplemental feeding provided rapid growth but were applied to only four subpopulations. As of 2023, recovery actions have increased the abundance of southern mountain caribou by 52%, compared to a simulation with no interventions. When predation pressure was reduced, rapid population growth was observed, even under contemporary climate change and high levels of habitat loss. Unless predation is reduced, caribou subpopulations will continue to be extirpated well before habitat conservation and restoration can become effective.


Citations (80)


... Image of a coyote (Canis latrans) attempting to capture a nine-banded armadillo (Dasypus novemcinctus) in the Wichita Mountains Wildlife Refuge, OK, USA (image collected during Snapshot USA 2022 sampling[29]). ...

Reference:

Habitat and Predator Influences on the Spatial Ecology of Nine-Banded Armadillos
SNAPSHOT USA 2019-2023: The First Five Years of Data From a Coordinated Camera Trap Survey of the United States

Global Ecology and Biogeography

... Conversely, if this mechanism were found to be numeric, it would suggest that anthropogenic mortality is additive to at least some degree. Human-caused mortality of gray wolves was recently found to be additive in YNP (Cassidy et al. 2024) and in the wolf population within YCRNP during lethal control periods in adjacent areas (Schmidt et al. 2017). As discussed in Cassidy et al. (2023) and noted in Cassidy et al. (2024), wolf population abundance can remain stable concurrent to negative impacts on wolf social dynamics at the pack level. ...

Harvest of transboundary grey wolves from Yellowstone National Park is largely additive

... The reserve is mostly forested, with coastal Mongolian oak (Quercus mongolica) and mixed hardwood forests shifting to forests of Korean pine (Pinus koraiensis) and deciduous species further inland. These forest transitions result in important spatial variation in mast crop availability for wildlife, as acorns and pine nuts are dominant sources of food for much of the wildlife community (Heptner, Nasimovich, and Bannikov 1988;Waller et al. 2024). Our study to estimate prey densities took place in a roughly 500 km 2 area within the southern portion of the Zapovednik. ...

Resource‐driven changes in wild boar movement and their consequences for the spread of African Swine Fever in the Russian Far East

... We assessed changing weather patterns as an alternate or additive explanation for the decline of migration. The density of caribou changed concurrently during our period of investigation, and these declines have also been linked to increasing disturbance (Apps et al. 2013;Lamb et al. 2024). We did not assess how migration was linked to changing population density due to the difficulty in reliably separating covarying processes (increasing disturbance and declining abundance) without a proper experimental design. ...

Effectiveness of population‐based recovery actions for threatened southern mountain caribou

... vary as a function of environmental conditions (Burton et al. 2024), we predicted that both species would demonstrate nocturnal diel activity patterns with a high degree of temporal overlap (Saldo et al. 2023). ...

Mammal responses to global changes in human activity vary by trophic group and landscape

Nature Ecology & Evolution

... There are now many international examples of Indigenous communities leading conservation projects or managing protected areas, and many conservationists who recognize the need for Indigenous leadership on traditional lands. However such projects are rarely described as "rewilding," except in passing (e.g., Heuer et al. 2023), and several have been reframed away from rewilding (see below). This may be because of a colonial taint that is perceived still to adhere to the rhetoric of wilderness and the wild, reinforced by rewilders' emphasis on the withdrawal of active and ongoing intervention and by their positioning of animal agency as an alternative to human agency, rather than a complement to it (Ward 2019). ...

Reintroducing bison to Banff National Park -an ecocultural case study

Frontiers in Conservation Science

... Other populations of resident elk also seem to leverage irrigated crops to offset the lower food quality available in their range during summer (Barker 2018). Given the plastic nature of elk movement tactics, the ratio of migrants and residents within herds may shift over time (Zuckerman et al. 2023), with pressures such as density-dependence and predation risk influencing prevalence (Hebblewhite and Merrill 2011;Williams et al. 2023). ...

Predation risk drives long‐term shifts in migratory behaviour and demography in a large herbivore population

... "Defend the core -grow the core" marks a shift toward preventative and coordinated management that prioritizes maintenance of intact grasslands at the scale of ecoregions rather than the historic reactive approach that focuses conservation efforts on attempting to restore highly degraded lands at fine scales (Roberts et al., 2018;Scholtz et al., 2021). The ecological support for this strategy rests on defending areas that are free of invasive woody plant propagules (Fogarty et al., 2022), deprioritizing heavily invaded areas due to rapid reinvasion potential and the high costs of restoring heavily invaded areas (Simonsen et al., 2015;Fogarty et al., 2021), and the fact that many grassland-dependent taxa require large-scale, intact grasslands (treeless, without row-crop agriculture) to persist (Tack et al., 2023). However, there is a need to test conservation outcomes of defend the coregrow the core. ...

Grassland intactness outcompetes species as a more efficient surrogate in conservation design

... In the context of a warming climate, the boreal forest is expected to have a higher proportion of deciduous vegetation (Boulanger and Pascual Puigdevall, 2021). This, combined with a progressive decrease in the extent of older forests because of increased disturbances, both from forest harvesting and natural origins, may be one of the major threats to the integrity of boreal communities (Cadieux et al., 2020;Cadieux and Drapeau, 2017;Carroll, 2007;Drapeau et al., 2000;Janssen et al., 2009;Labadie et al., 2024a). Yet, there has been little focus on the variability among birds in their responses to these interacting environmental pressures. ...

The umbrella value of caribou management strategies for biodiversity conservation in boreal forests under global change

The Science of The Total Environment

... Moose (Alces alces; moswa in Cree) are an important, but declining, subsistence resource for many First Nations of Canada (Kuzyk et al. 2018;Natcher et al. 2021;Priadka et al. 2022;Ross and Mason 2020) and there is widespread recognition that resource extraction impacts moose population dynamics, distributions, and predation rates in Alberta (Lamy and Finnegan 2019;Neilson and Boutin 2017). In the boreal, moose select for habitat that provides security when predator abundance is high (Ethier et al. 2024), and have lower occurrence in areas with pipelines, seismic lines, 3D seismic lines, unpaved roads, and new cut blocks (Dickie et al. 2022;Finnegan et al. 2023;Fisher et al. 2021;Finnegan 2023, 2022), which are often used by predators. This suggests that perceived predation risk is a strong driver of habitat selection, especially in areas with high human use. ...

Whose line is it anyway? Moose (Alces alces) response to linear features