Katherine Zeller

Dr. Katherine Zeller

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Research Focus & Metrics

Academic Career Length

15Years (2012-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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11 April 2012 in Landscape Ecology
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Journal Article
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KZKatherine Zeller
Katherine Zeller
KMKevin McGarigal
Kevin McGarigal
AWAndrew R. Whiteley
Andrew R. Whiteley

25 March 2018 in Diversity and Distributions
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Journal Article
Closed access
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KZKatherine Zeller
Katherine Zeller
Megan JenningsMegan Jennings
Megan Jennings
TVT. Winston Vickers
T. Winston Vickers
HEHolly B. Ernest
Holly B. Ernest
SCSamuel A. Cushman
Samuel A. Cushman
WBWalter M. Boyce
Walter M. Boyce

31 January 2014 in Landscape Ecology
Verified
Journal Article
Closed access
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KZKatherine Zeller
Katherine Zeller
KMKevin McGarigal
Kevin McGarigal
PBPaul Beier
Paul Beier
SCSamuel A. Cushman
Samuel A. Cushman
TVT. Winston Vickers
T. Winston Vickers
WBWalter M. Boyce
Walter M. Boyce

2 November 2015 in Landscape Ecology
Verified
Journal Article
Closed access
PDF file
KZKatherine Zeller
Katherine Zeller
KMKevin McGarigal
Kevin McGarigal
SCSamuel A. Cushman
Samuel A. Cushman
PBPaul Beier
Paul Beier
TVT. Winston Vickers
T. Winston Vickers
WBWalter M. Boyce
Walter M. Boyce

13 June 2017 in PLOS ONE
Verified
Journal Article
Open access
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KZKatherine Zeller
Katherine Zeller
TVT Winston Vickers
T Winston Vickers
HEHolly B Ernest
Holly B Ernest
WBWalter M Boyce
Walter M Boyce
The importance of examining multiple hierarchical levels when modeling resource use for wildlife has been acknowledged for decades. Multi-level resource selection functions have recently been promoted as a method to synthesize resource use across nested organizational levels into a single predictive surface. Analyzing multiple scales of selection within each hierarchical level further strengthens multi-level resource selection functions. We extend this multi-level, multi-scale framework to modeling resistance for wildlife by combining multi-scale resistance surfaces from two data types, genetic and movement. Resistance estimation has typically been conducted with one of these data types, or compared between the two. However, we contend it is not an either/or issue and that resistance may be better-modeled using a combination of resistance surfaces that represent processes at different hierarchical levels. Resistance surfaces estimated from genetic data characterize temporally broad-scale dispersal and successful breeding over generations, whereas resistance surfaces estimated from movement data represent fine-scale travel and contextualized movement decisions. We used telemetry and genetic data from a long-term study on pumas (Puma concolor) in a highly developed landscape in southern California to develop a multi-level, multi-scale resource selection function and a multi-level, multi-scale resistance surface. We used these multi-level, multi-scale surfaces to identify resource use patches and resistant kernel corridors. Across levels, we found puma avoided urban, agricultural areas, and roads and preferred riparian areas and more rugged terrain. For other landscape features, selection differed among levels, as did the scales of selection for each feature. With these results, we developed a conservation plan for one of the most isolated puma populations in the U.S. Our approach captured a wide spectrum of ecological relationships for a population, resulted in effective conservation planning, and can be readily applied to other wildlife species.

29 August 2020 in Land
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Journal Article
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KZKatherine Zeller
Katherine Zeller
Rebecca LewisonRebecca Lewison
Rebecca Lewison
RFRobert J. Fletcher
Robert J. Fletcher
MTMirela G. Tulbure
Mirela G. Tulbure
Megan JenningsMegan Jennings
Megan Jennings
Landscape connectivity is increasingly promoted as a conservation tool to combat the negative effects of habitat loss, fragmentation, and climate change. Given its importance as a key conservation strategy, connectivity science is a rapidly growing discipline. However, most landscape connectivity models consider connectivity for only a single snapshot in time, despite the widespread recognition that landscapes and ecological processes are dynamic. In this paper, we discuss the emergence of dynamic connectivity and the importance of including dynamism in connectivity models and assessments. We outline dynamic processes for both structural and functional connectivity at multiple spatiotemporal scales and provide examples of modeling approaches at each of these scales. We highlight the unique challenges that accompany the adoption of dynamic connectivity for conservation management and planning in the context of traditional conservation prioritization approaches. With the increased availability of time series and species movement data, computational capacity, and an expanding number of empirical examples in the literature, incorporating dynamic processes into connectivity models is more feasible than ever. Here, we articulate how dynamism is an intrinsic component of connectivity and integral to the future of connectivity science.