Cited by 148Wildlife-Road Interactions and ConservationWildlife Ecology and ConservationSpecies Distribution and Climate Change

The DOI matches its Crossref record; 22 of the 23 references it cites were found in a registry or an index; none of the 8 sources its claims cite is checked for support yet.

The Effect of Map Boundary on Estimates of Landscape Resistance to Animal Movement

Open access

Abstract

BACKGROUND: Artificial boundaries on a map occur when the map extent does not cover the entire area of study; edges on the map do not exist on the ground. These artificial boundaries might bias the results of animal dispersal models by creating artificial barriers to movement for model organisms where there are no barriers for real organisms. Here, we characterize the effects of artificial boundaries on calculations of landscape resistance to movement using circuit theory. We then propose and test a solution to artificially inflated resistance values whereby we place a buffer around the artificial boundary as a substitute for the true, but unknown, habitat. METHODOLOGY/PRINCIPAL FINDINGS: We randomly assigned landscape resistance values to map cells in the buffer in proportion to their occurrence in the known map area. We used circuit theory to estimate landscape resistance to organism movement and gene flow, and compared the output across several scenarios: a habitat-quality map with artificial boundaries and no buffer, a map with a buffer composed of randomized habitat quality data, and a map with a buffer composed of the true habitat quality data. We tested the sensitivity of the randomized buffer to the possibility that the composition of the real but unknown buffer is biased toward high or low quality. We found that artificial boundaries result in an overestimate of landscape resistance. CONCLUSIONS/SIGNIFICANCE: Artificial map boundaries overestimate resistance values. We recommend the use of a buffer composed of randomized habitat data as a solution to this problem. We found that resistance estimated using the randomized buffer did not differ from estimates using the real data, even when the composition of the real data was varied. Our results may be relevant to those interested in employing Circuitscape software in landscape connectivity and landscape genetics studies.

Overview

AI snapshot

Written from the paper’s full text.

TL;DR

Artificial map boundaries inflate landscape resistance estimates from circuit theory, and adding a buffer around the boundary reduces this bias. A buffer of randomized habitat data performed similarly to a buffer of true habitat data, even when the true buffer was biased toward low or high quality.

Key findings

  • Resistance was overestimated with no buffer relative to a real-data buffer for sites in both the inner core (Cohen’s d = 1.50) and outer core (d = 0.90).
  • Resistance estimates using a randomized buffer did not differ from estimates using a real-data buffer for inner-core sites (d = 0.13) or outer-core sites (d = 0.002).
  • No-buffer maps also overestimated resistance relative to low-biased buffers (inner d = 0.75; outer d = 0.84) and high-biased buffers (inner d = 0.90; outer d = 0.90).
  • Randomized-buffer estimates remained close to low-biased buffers (inner d = 0.28; outer d = 0.37) and high-biased buffers (inner d = 0.15; outer d = 0.23).

Methods

  • The authors used circuit theory via CIRCUITSCAPE 3.5 on a forest resource inventory map of Ontario, Canada, reclassified for American marten (*Martes americana*) habitat quality from 1 (low) to 3 (high).
  • They used 5 replicate 10,000-km² plots, each with a 2,500-km² core and a 25-km buffer; pixels were 0.0625 km² (160,000 pixels per plot). They estimated resistance between source and destination sites 10 km apart, with 10 random pairs in each inner and outer core per plot (n = 100 pairs), then pooled data over plots for comparisons (n = 50).
  • They compared five scenarios—no buffer, real buffer, randomized buffer, low-biased buffer, and high-biased buffer—using Cohen’s d for paired comparisons, interpreting d = 0.2 as small, 0.5 as medium, and 0.8 as large.

Limitations

  • Stated in the paper: the results are based on a relatively simple plot design with a direct path between sites and no barriers or narrow habitat passages; artificial boundaries may have a greater effect in more complex landscapes.
  • Stated in the paper: buffer width and composition are project-specific and may be arbitrary when habitat quality beyond the map is unknown; Circuitscape memory limitations may restrict grids larger than six million cells.
  • Stated in the paper: future work is needed on the sensitivity of circuit theory to varying levels of landscape connectivity; the study used simulated data and effect sizes rather than test statistics.

Model-written summary. Check it against the paper before relying on it.

Integrity signals

Registry

Crossref · 10.1371/journal.pone.0011785

Cites

22 of 22 references verified0 citation errors · 0 not checkable

Statistics

Nothing to recompute.

Verification

Claims the paper makes

0 of 8 cited sources checked · 0 supported · 0 flagged

  • Findingown data

    Resistance estimates using the randomized buffer did not differ from estimates using the real buffer for sites in both inner and outer cores.

    “When we used the randomized buffer however, resistance estimates were not different than estimates using a buffer of real data for sites in either the inner (d = 0.13) or outer (d = 0.002) cores, as indicated by small effect sizes (Table 2).”
    Quote in the paperSubstantial claim
  • Findingown data

    Resistance estimates using the randomized buffer did not differ from estimates using the high-biased buffer for sites in both inner and outer cores.

    “We found no difference in resistance however, between scenarios with a buffer of randomized data and a buffer biased towards high quality, for sites in both the inner (d = 0.15) and outer (d = 0.23) cores, as indicated by small effect sizes (Table 2).”
    Quote in the paperSubstantial claim
  • Findingown data

    In the no-buffer scenario, landscape resistance was overestimated relative to the real-buffer scenario for sites in both inner and outer cores.

    “Resistance was overestimated in the scenario with no buffer relative to the buffer of real data (Figures 4–5) for sites in both the inner (d = 1.50) and outer (d = 0.90) cores, as indicated by large effect sizes (Table 2).”
    Quote in the paperSubstantial claim
  • Findingown data

    In the no-buffer scenario, resistance was overestimated relative to the high-biased buffer for sites in both inner and outer cores.

    “We found that the scenario with no buffer overestimated resistance relative to when we biased the real buffer toward high habitat quality, for both the inner (d = 0.90) and outer (d = 0.90) cores (Table 2).”
    Quote in the paperSubstantial claim
  • Findingown data

    In the no-buffer scenario, resistance was overestimated relative to the low-biased buffer for sites in both inner and outer cores.

    “Resistance was again overestimated for the scenario with no buffer relative to the buffer biased towards low quality for sites in both the inner (d = 0.75) and outer (d = 0.84) cores (Table 2).”
    Quote in the paperSubstantial claim
  • It may state two separate claims as one. 3
  • Probably not a substantial claim. 2
  • It may state two separate claims as one.

    Interpretationreasoning

    A buffer around the artificial boundary removes the barrier to movement and produces a more accurate estimate of resistance.

    “A buffer around the artificial boundary removed the barrier to movement and produced a more accurate estimate of resistance.”
    Quote in the paperSubstantial claim
  • Probably not a substantial claim.

    Premisereasoning

    Artificial boundaries of a map arise in studies that span large areas where compatible remotely-sensed land-cover data might not exist for the entire region of interest.

    “Artificial boundaries of a map, boundaries that exist on the land-cover map but not on the ground, will arise in studies that span large areas where compatible remotely-sensed land-cover data might not exist for the entire region of interest.”
    Quote in the paperSubstantial claim
  • Probably not a substantial claim. The paper’s conclusions may not depend on it.

    Premisecitation

    Circuit theory is an appealing model because it uses random walkers to model overall resistance to movement rather than discrete paths.

    “One of the reasons circuit theory is appealing as a model of gene flow and individual movement is that the incorporation of random walkers on networks to estimate landscape resistance allows resistance to decrease with increasing connectivity, path width, and path redundancy [11], [14].”
    Quote in the paperNot a substantial claim0 of 2 sources checked
    • cites [11] BH McRae, 2008, Using circtuit theory to model connectivity in ecology, evolution, and conservation., Ecology source
    • cites [14] BH McRae, 2006, Isolation by resistance., Evolution source
  • It may state two separate claims as one.

    Interpretationreasoning

    Artificial boundaries limit the space available to random walkers, which reduces the number of paths to each node and thus increases perceived resistance.

    “This is because artificial boundaries limit the space available to random walkers, which artificially reduces the number of paths to each node, thus increasing perceived resistance.”
    Quote in the paperSubstantial claim
  • It may state two separate claims as one.

    Premisecitation

    Several authors have alluded to the idea that artificial boundaries might influence the results of least cost path and landscape resistance models, but no one has directly addressed the issue.

    “Several authors have alluded to the idea that artificial boundaries might influence the results of least cost path and landscape resistance models [2], [11], [15]–[18], but to our knowledge, no one has directly addressed the issue.”
    Quote in the paperSubstantial claim0 of 6 sources checked
    • cites [2] P Beier, 2008, Forks in the road: Choices in procedures for designing wildland linkages., Conserv Biol source
    • cites [11] BH McRae, 2008, Using circtuit theory to model connectivity in ecology, evolution, and conservation., Ecology source
    • cites [15] F Adriaensen, 2003, The application of ‘least-cost’ modelling as a functional landscape model., Landscape Urban Plan source
    • cites [16] G Verbeylen, 2003, Does matrix resistance influence red squirrel (Sciurus vulgaris L. 1758) distribution in an urban landscape?, Landscape Ecol source
    • cites [17] L Pascual-Hortal, 2007, Impact of spatial scale on the identification of critical habitat patches for the maintenance of landscape connectivity., Landscape Urban Plan source
    • cites [18] JA Lee-Yaw, 2009, Do landscape processes predict phylogeographic patterns in the wood frog?, Mol Ecol source
5 of 5
  • The paper relies on this without support.

    The outcome of the simulation is not species or landscape specific.

    “The species of interest and area of study that we used for our simulation is irrelevant however, as we did not expect the outcome to be either species or landscape specific.”
  • The authors state this as an assumption.

    The true habitat composition beyond the map boundaries is unknown.

    “This buffer was a substitute for the true data in scenario 2 (assuming the true data were unknown).”
2 of 2

Claims other papers make about this one

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Citations

Cites

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1 of the 23 references couldn’t be matched to a known paper.

Research works printed but not linked: 1

  1. J Cohen, 1988, Statistical power analysis for the behavioral sciences, 2nd edition.

Cited by

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Metadata

Authors
Koen, E. L., Garroway, C. J., Wilson, P. J., & Bowman, J.
Affiliations
  • Trent University (CA)
  • Ministry of Natural Resources and Forestry (CA)
Corresponding author
Koen, Erin L.
Venue
PLoS ONE
Published
2010-07-26
Volume
5
Issue
7
Pages
e11785
ISSN
1932-6203 (ISSN-L)
OpenAlex
W2167189097
Cited by
148
References
23
Citations by year
2026: 7 · 2025: 13 · 2024: 8 · 2023: 18 · 2022: 9 · 2021: 9 · 2020: 13 · 2019: 7 · 2018: 6 · 2017: 17 · 2016: 10 · 2015: 11 · 2014: 6 · 2013: 5 · 2012: 5
FWCI
3.72
Type
journal article
Language
en
Open access
Locations
  • PLoS ONE (publishedVersion, cc-by)
  • PubMed Central (publishedVersion, cc-by)
  • PubMed (publishedVersion)
  • RePEc: Research Papers in Economics (submittedVersion)
  • DOAJ (DOAJ: Directory of Open Access Journals) (submittedVersion, cc-by-sa)
Funders
Natural Sciences and Engineering Research Council of Canada
Topics
  • Physical Sciences › Environmental Science › Ecology › Wildlife-Road Interactions and Conservation
  • Physical Sciences › Environmental Science › Ecology › Wildlife Ecology and Conservation
  • Physical Sciences › Environmental Science › Ecological Modeling › Species Distribution and Climate Change
Keywords
circuit theory, Circuitscape, gene flow, animal dispersal, buffer zones, habitat quality, landscape connectivity, landscape genetics
MeSH terms
Animals, Canada, Geography, Models, Theoretical, Ontario, Ecosystem

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