Modeling the invasive emerald ash borer risk of spread using a spatially explicit cellular model

Prasad, Anantha; Iverson, Louis R.; Peters, Matthew P.; Bossenbroek, Jonathan M.; Matthews, Stephen N.; Sydnor, T. Davis; Schwartz, Mark W.

doi:10.1007/s10980-009-9434-9

Cited by 144 publications

(115 citation statements)

References 33 publications

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“…Black ash carries more risk because, among other disadvantageous traits, it has low resistance to the emerald ash borer (Agrilus planipennis Fairmaire), which currently threatens all ash species in North America (Prasad et al 2010). White oak is expected to gain habitat in northern Wisconsin, because it is well adapted to drier conditions and increased disturbance.…”

Section: Preparing For Climate Changementioning

confidence: 99%

Effects of climatic variability and change on forest ecosystems: a comprehensive science synthesis for the U.S

Vose¹,

Peterson²,

Patel-Weynand³

2012

104

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Section: Preparing For Climate Changementioning

confidence: 99%

Effects of climatic variability and change on forest ecosystems: a comprehensive science synthesis for the U.S

Vose¹,

Peterson²,

Patel-Weynand³

2012

104

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“…and accelerating rates of spread (Clark, 1998;Bossenbroek et al, 2001;Clark et al, 2001;Muirhead et al, 2006;Prasad et al, 2010). However, since control strategies focus on satellite populations in an effort to slow the spread, a better understanding of local dispersal behavior in these satellite populations is required (Mercader et al, 2009(Mercader et al, , 2011bMcCullough and Mercader, 2012).…”

Section: Introductionmentioning

confidence: 99%

Integrodifference equations in patchy landscapes

Musgrave

Lutscher

2013

J. Math. Biol.

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In this dissertation, we study integrodifference equations in patchy landscapes. Specifically, we provide a framework for linking individual dispersal behavior with populationlevel dynamics in patchy landscapes by integrating recent advances in modeling dispersal into an integrodifference equation.First, we formulate a random-walk model in a patchy landscape with patchdependent diffusion, settling, and mortality rates. We incorporate mechanisms for individual behavior at an interface which, in general, results in the probability-density function of the random walker being discontinuous at an interface. We show that the dispersal kernel can be characterized as the Green's function of a second-order differential operator and illustrate the kind of (discontinuous) dispersal kernels that arise from our approach. We examine the dependence of obtained kernels on model parameters.Secondly, we analyze integrodifference equations in patchy landscapes equipped with discontinuous kernels. We obtain explicit formulae for the critical-domain-size problem, as well as explicit formulae for the analogous critical size of good patches on an infinite, periodic, patchy landscape. We examine the dependence of obtained formulae on individual behavior at an interface. Through numerical simulations, we observe that, if the population can persist on an infinite, periodic, patchy landscape, its spatial profile can evolve into a discontinuous traveling periodic wave. We derive a dispersion relation for the speed of the wave and illustrate how interface behavior ii

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“…Road networks similarly played an important role in distributing emerald ash borer (Agrilus planipennis) throughout Ohio, with 84 % of new sites occurring within 1 km of roads [50]. That said, road characteristics can mediate the extent to which they facilitate dispersal.…”

Section: Landscape Features That Act As Hubs Corridors or Barriersmentioning

confidence: 99%

Direct and Indirect Interactions between Landscape Structure and Invasive or Overabundant Species

Rodewald

Arcese

2016

Curr Landscape Ecol Rep

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We reviewed recent literature to evaluate interactions between landscape structure (i.e., composition and configuration of landscapes) and overabundant and/or invasive species or Bundesirable^species. Undesirable species are strongly associated with fragmented landscapes, especially those with linearly arranged elements to facilitate dispersal, and with land uses that serve as population sources. In some cases, structural legacies, such as land use histories, were as important as current landscape patterns. Many undesirable species also influenced landscape structure by altering disturbance regimes via a wide range of abiotic and biotic mechanisms, including by affecting abundance of keystone, foundation or engineering species at landscape scales, and by changing species interactions in ways that prompted community-level changes. In some instances, the effects of species on landscapes facilitated invasion and/or population growth to establish positive feedback cycles. Understanding the reciprocal effects of landscape pattern on invasive and overabundant species can help guide effective management strategies by increasing the cost-efficiency of conservation investments and prioritizing conservation actions.

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Modeling the invasive emerald ash borer risk of spread using a spatially explicit cellular model

Cited by 144 publications

References 33 publications

Effects of climatic variability and change on forest ecosystems: a comprehensive science synthesis for the U.S

Effects of climatic variability and change on forest ecosystems: a comprehensive science synthesis for the U.S

Integrodifference equations in patchy landscapes

Direct and Indirect Interactions between Landscape Structure and Invasive or Overabundant Species

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