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Context Species-specific models of landscape capability (LC) can inform landscape conservation design. Landscape capability is “the ability of the landscape to provide the environment […] and the local resources […] needed for survival and reproduction […] in sufficient quantity, quality and accessibility to meet the life history requirements of individuals and local populations.” Landscape capability incorporates species’ life histories, ecologies, and distributions to model habitat for current and future landscapes and climates as a proactive strategy for conservation planning. Objectives We tested the ability of a set of LC models to explain variation in point occupancy and abundance for seven bird species representative of spruce-fir, mixed conifer-hardwood, and riparian and wooded wetland macrohabitats. Methods We compiled point count data sets used for biological inventory, species monitoring, and field studies across the northeastern United States to create an independent validation data set. Our validation explicitly accounted for underestimation in validation data using joint distance and time removal sampling. Results Blackpoll warbler (Setophaga striata), wood thrush (Hylocichla mustelina), and Louisiana (Parkesia motacilla) and northern waterthrush (P. noveboracensis) models were validated as predicting variation in abundance, although this varied from not biologically meaningful (1%) to strongly meaningful (59%). We verified all seven species models [including ovenbird (Seiurus aurocapilla), blackburnian (Setophaga fusca) and cerulean warbler (Setophaga cerulea)], as all were positively related to occupancy data. Conclusions LC models represent a useful tool for conservation planning owing to their predictive ability over a regional extent. As improved remote-sensed data become available, LC layers are updated, which will improve predictions.
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RESEARCH ARTICLE
Landscape capability models as a tool to predict fine-scale
forest bird occupancy and abundance
Zachary G. Loman .William V. Deluca .Daniel J. Harrison .
Cynthia S. Loftin .Brian W. Rolek .Petra B. Wood
Received: 25 April 2017 / Accepted: 6 October 2017 / Published online: 16 October 2017
Springer Science+Business Media B.V. 2017
Abstract
Context Species-specific models of landscape capa-
bility (LC) can inform landscape conservation design.
Landscape capability is ‘the ability of the landscape to
provide the environment [] and the local resources
[] needed for survival and reproduction []in
sufficient quantity, quality and accessibility to meet
the life history requirements of individuals and local
populations.’ Landscape capability incorporates spe-
cies’ life histories, ecologies, and distributions to
model habitat for current and future landscapes and
climates as a proactive strategy for conservation
planning.
Objectives We tested the ability of a set of LC
models to explain variation in point occupancy and
abundance for seven bird species representative of
spruce-fir, mixed conifer-hardwood, and riparian and
wooded wetland macrohabitats.
Methods We compiled point count data sets used for
biological inventory, species monitoring, and field
studies across the northeastern United States to create
an independent validation data set. Our validation
explicitly accounted for underestimation in validation
data using joint distance and time removal sampling.
Results Blackpoll warbler (Setophaga striata), wood
thrush (Hylocichla mustelina), and Louisiana (Parke-
sia motacilla) and northern waterthrush (P. novebo-
racensis) models were validated as predicting
variation in abundance, although this varied from not
biologically meaningful (1%) to strongly meaningful
Electronic supplementary material The online version of
this article (doi:10.1007/s10980-017-0582-z) contains supple-
mentary material, which is available to authorized users.
Z. G. Loman (&)D. J. Harrison B. W. Rolek
Department of Wildlife Fisheries and Conservation
Biology, University of Maine, 5755 Nutting Hall, Room
210, Orono, ME 04469, USA
e-mail: zachary.loman@maine.edu
W. V. Deluca
Department of Environmental Conservation, University of
Massachusetts, 160 Holdsworth Way, Amherst,
MA 01003, USA
C. S. Loftin
Maine Cooperative Fish and Wildlife Research Unit, U.S.
Geological Survey, 5755 Nutting Hall, Room 210, Orono,
ME 04469, USA
P. B. Wood
U.S. Geological Survey, West Virginia Cooperative Fish
and Wildlife Research Unit, West Virginia University,
P. O. Box 6125, 322 Percival Hall, Morgantown,
WV 26506, USA
123
Landscape Ecol (2018) 33:77–91
https://doi.org/10.1007/s10980-017-0582-z
Content courtesy of Springer Nature, terms of use apply. Rights reserved.
... To test these questions, we used the representative (i.e., proxy) species framework informing conservation at broad spatial scales devised by the North Atlantic Landscape Conservation Cooperative (NALCC). We sought to understand how models of proxy species' landscape capability (LC;McGarigal et al. 2016;Loman et al. 2017a) could best be used as proxies for represented species. LC models were created to predict the spatially-explicit capability of the landscape to support focal species (McGarigal et al. 2016), and they were designed to be useful at local scales (tens of meters to thousands of hectares; Poiani et al. 2000). ...
... We excluded detections at distances greater than 100 m when determining point occurrence. We used 30,065 point counts at 10,122 discrete spatially referenced locations that met our criteria (Loman et al. 2017a) to evaluate the following objectives. The first objective is the primary goal, with the subsequent objectives intended to provide additional clarity, or to answer additional questions that arose during analyses (Fig. 3). ...
... It should be considered that we tested the relationships at the finest scales possible given the survey methods (100 m survey radius) and that covariance in occurrence is scale-dependent with correlations that often are weaker at finer rather than broader scales (Weaver 1995;Prendergast and Eversham 1997). Predictive ability of even the best proxy LC model used to predict a represented species (67% accurate) typically was less than a LC model at predicting its own species' occurrence (i.e., not used as a proxy; range 62-90%; Loman et al. 2017a). Thus, while improving the proxyrepresented species pair is likely useful, it is not surprising that development of a larger suite of proxy models and reducing the number of proxy-represented species pairs will provide more accurate and precise predictions. ...
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Context Proxy species, which represent suites of organisms with similar habitat requirements, are common in conservation. Landscape Capability (LC) models aim to quantify the spatially-explicit capability of landscapes to support proxy species that represent suites of forest birds. Objectives We evaluated the North Atlantic Landscape Conservation Cooperative (NALCC) proxy models of LC and represented species framework across 13 states in the northeastern United States from Virginia to Maine. We validated a suite of questions related to co-occurrence of proxy and represented species with a compilation of independent datasets. Methods We tested proxy species LC models ability to explain represented species’ occurrences, including using multiple proxies together, and benchmarked against empirical data and land cover type classifications. We tested effect of several factors on predictive ability including relative range overlap and ecological and taxonomic dissimilarity between proxy and represented species. Results LC models performed variably, but represented species occurrences were rarely predicted as accurately as proxy species. Models improved predictions over macrohabitat classifications. Using multiple proxies together occasionally improved predictions of represented species. Considerable range overlap was needed for models to be predictive of represented species. Ecological and taxonomic similarity had no effect on predictive ability. LC models worked similarly to using empirical observations, suggesting shortcomings were because of imperfect surrogacy. Conclusions Conservation proxies as representatives of species groups that are associated with macrohabitats are useful, but empirical data are necessary to evaluate proxy species’ effectiveness. Habitat-based models can provide similar predictive ability as empirical observations of proxies and represent a useful tool in conservation planning.
... Detection probabilities ≥0.9 have been reported for ACFL in harvested and unharvested forests (Farnsworth et al. 2002;Twedt and Wilson 2017). In unharvested forests, reported detection probabilities for LOWA ranged from 0.7 to ≥0.9 (Loman et al. 2018;Reidy, Thompson, and Bailey 2011). Estimates of BHVI detection probability are sparse in the literature, and only one estimate for the species' detection probability near streams in Appalachian-hardwood forests has been reported (0.25-0.5; ...
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... However, due to the lack of spatially explicit report data on the oak decline sites and associated environmental characteristics, risk assessment and mapping at landscape and regional scales are challenging, as researchers in other systems have also noted [22,23]. Other studies have successfully combined remote sensing and ground truthing to strengthen resulting models in a variety of systems and for different purposes, from mapping land cover [24] to testing models of habitat suitability [25]. Risk maps for tree health issues that use GIS and satellite information have been developed in a number of contexts, such as forest fire and disease spread [26,27]. ...
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Oak decline is a general term used for the progressive dieback and eventual mortality of oak trees due to many compounding stressors, typically a combination of predisposing, inciting, and contributing factors. While pinpointing individual causes of decline in oak trees is a challenge, past studies have identified site and stand characteristics associated with oak decline. In this study, we developed a risk map of oak decline for the Daniel Boone National Forest (DBNF), combining GIS, remote sensing (RS), and public reporting (citizen science, CS). Starting with ground reports of decline (CS), we developed a site-scale model (GIS and RS) for oak decline based on four previously identified predisposing factors: elevation, slope, solar radiation, and topographic wetness. We found that areas identified in the model as having a high oak decline risk also reflected areas of observed oak decline (CS). We then optimized and expanded this risk model to the entire range of the DBNF, based on both site characteristics (as piloted for the case study site) and stand inventory data. The stand inventory data (including species composition and age) further improved the model, resulting in a risk map at the landscape level. This case study can serve as a planning tool and highlights the potential usefulness of integrating GIS, remote sensing, and citizen science.
... While these simple correlative models used only climatic variables, further analysis with more sophisticated models has similarly projected declines in the suitability of boreal birds in northeastern United States in the coming decades. McGarigal et al. [34] used climate, habitat, and land use variables to calculate and project changes in Landscape Capability, an index reflecting the ability of the landscape to meet species' breeding season natural history requirements [35]. There was a projected 64% decline in Landscape Capability for Blackpoll Warbler across northeastern United States by 2080, along with a predicted upslope shift in distribution greater than 100 m. ...
Article
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Many North American boreal forest birds reach the southern periphery of their distribution in the montane spruce–fir forests of northeastern United States and the barren coastal forests of Maritime Canada. Because the southern periphery may be the first to be impacted by warming climates, these populations provide a unique opportunity to examine several factors that will influence the conservation of this threatened group under climate change. We discuss recent research on boreal birds in Northeastern US and in Maritime Canada related to genetic diversity, population trends in abundance, distributional shifts in response to climate change, community composition, and threats from shifting nest predators. We discuss how results from these studies may inform the conservation of boreal birds in a warming world as well as open questions that need addressing.
... It is often selected as an efficient metric for modeling ecological networks and maintaining biodiversity by using focal species, although usually empirical evidence is insufficient to verify the focal species [44,45]. However, studies considering the dispersal ability of the whole bird communities are still lacking, because information about their dispersal ability based on empirical evidence is limited in existing research [41,46]. ...
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Understanding how environmental changes driven by urbanization impact the biodiversity in urban riparian areas has great importance for landscape planning and river ecosystem conservation. There have been many studies on the response of bird communities to different environmental variables in urban parks; however, although supporting some of the highest bird diversities, case studies in urban riparian areas remain limited. In existing research, few studies have considered the impact of both local waterfront characteristics and surrounding environmental variables at a larger scale. In this study, we selected birds as the indicator to clarify their response to both local- and landscape-scale environmental variables in riparian areas of Tsing river, Beijing, in terms of (a) vegetation composition, (b) human disturbance, (c) land cover, and (d) landscape connectivity. We hypothesized that birds with different biological characteristics may respond differently to environmental variables. Birds were then further grouped according to the habitat type, residential type, and feeding type. It turned out that the coverage of grass and the disturbance of pedestrians are the most influential variables. Besides, compared with the land cover and landscape connectivity, the total contribution of vegetation characteristics and human disturbance accounts for the main proportion of explained variance. Information pertaining to these environmental variables can provide evidence to support bird conservation efforts in urban areas, and the identified distance threshold provides a basis for future landscape connectivity assessments.
... Due to the strong relationship between elevation and precipitation in our study region (as noted above), we tested the relationship that the downscaled and interpolated precipitation values increase with elevation across our bird sampling locations with a linear regression model. These precipitation data are incorporated in fine-scale wildlife species distribution models and have been evaluated and used by the US Fish and Wildlife Service to inform landscape conservation design (Loman et al., 2017(Loman et al., , 2018. ...
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... To be most effective, conservation network planning would include: 1) a good understanding of habitat requirements for the species of interest, including how variation in habitat types, amounts, and juxtapositions influence population growth [14]; 2) a method for translating knowledge of habitat requirements into a spatially-explicit map representing variation in habitat suitability at a scale relevant to the species [15,16]; 3) an understanding of each species' adaptive demographic response to multiple networks under both current and future conditions; and 4) performance metrics that can be used to rank networks in terms of their relative risk to species persistence or likelihood of achieving desired conservation outcomes. Conservation network planning typically uses a variety of modeling tools to determine species' habitat and resource requirements [17,18]. For evaluating potential critical habitat for the spotted owl, we chose this approach to provide decision makers with a set of scientifically defensible outputs from a series of plausible scenarios (viz., changes in habitat suitability and barred owl [S. ...
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... To be most effective, conservation network planning would include: 1) a good understand- ing of habitat requirements for the species of interest, including how variation in habitat types, amounts, and juxtapositions influence population growth [14]; 2) a method for translating knowledge of habitat requirements into a spatially-explicit map representing variation in habi- tat suitability at a scale relevant to the species [15,16]; 3) an understanding of each species' adaptive demographic response to multiple networks under both current and future condi- tions; and 4) performance metrics that can be used to rank networks in terms of their relative risk to species persistence or likelihood of achieving desired conservation outcomes. Conserva- tion network planning typically uses a variety of modeling tools to determine species' habitat and resource requirements [17,18]. For evaluating potential critical habitat for the spotted owl, we chose this approach to provide decision makers with a set of scientifically defensible outputs from a series of plausible scenarios (viz., changes in habitat suitability and barred owl [S. ...
Conference Paper
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