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  • 1
    Online Resource
    Online Resource
    Berlin, Heidelberg :Springer Berlin / Heidelberg,
    Keywords: Spatial ecology-Mathematical models. ; Electronic books.
    Type of Medium: Online Resource
    Pages: 1 online resource (393 pages)
    Edition: 1st ed.
    ISBN: 9783642354977
    Series Statement: Lecture Notes in Mathematics Series ; v.2071
    DDC: 581.788
    Language: English
    Note: Intro -- Dispersal, Individual Movement and Spatial Ecology -- A Mathematical Perspective -- Foreword -- References -- Preface -- Contents -- Part I Individual Animal Movement -- Stochastic Optimal Foraging Theory -- 1 Introduction -- 2 Some Preliminary Assumptions of the Model -- 3 Calculation of < -- L> -- and < -- |l|> -- -- 4 Discrete Space Calculation -- 5 Lévy Random Searchers -- 6 Search Diffusivity -- 6.1 Characterizing First-Passage-Time Diffusivity -- 6.2 Characterizing Search Dynamics Diffusivity -- 7 Search in Heterogeneous Landscapes: Distributions of Starting Points -- 8 Discussion -- References -- Lévy or Not? Analysing Positional Data from Animal Movement Paths -- 1 Introduction -- 1.1 Lévy Walks -- 1.2 Correlated Random Walks and Composite Strategies -- 1.3 Determining Movement Processes from Observational Data -- 2 Sampling and Processing of Movement Path Data -- 2.1 Discrete Time Sampling -- 2.2 Identification of Turning Points -- 3 Analysing Data from a Composite Correlated Random Walk -- 3.1 The Composite Correlated Random Walk Model -- 3.2 Fitting a Composite Exponential Distribution -- 3.3 Testing Step Length Data -- 3.4 Testing Uniformity of Turning Angles -- 4 Discussion -- References -- Beyond Optimal Searching: Recent Developments in the Modelling of Animal Movement Patterns as Lévy Walks -- 1 Introduction -- 2 Underlying Mechanisms: The Key to Prediction and Understanding -- 2.1 Serial Correlation -- 2.2 Random Reorientation at Cues Left by Correlated Random Walkers -- 2.3 Lévy Walks as by Products of Advantageous Foraging Behaviours -- 2.4 Innate Physiology -- 3 Translating Observations Taken at Small Spatiotemporal Scales into Expected Patterns at Greater Scales -- 4 Enlarging the Framework of Lévy Walk Search Theory -- 4.1 Balancing the Demands of Foraging and Safety from Predation -- 4.2 Red Queen Dynamics. , 4.3 Intermittent Searches -- 4.4 Optimizing the Encounter Rate in Biological Interactions -- 5 Some Closing Remarks and Some Open Questions -- 5.1 Opening the Lévy Gates -- 5.2 Lévy Walks in Collective Motions: How the Blind Could Lead the Blind -- 5.3 Mathematical Challenges -- References -- Part II From Individuals to Populations -- The Mathematical Analysis of Biological Aggregation and Dispersal: Progress, Problems and Perspectives -- 1 Introduction -- 2 An Overview of Population-Level Descriptions -- 2.1 A Summary of the Levels of Description -- 2.2 The Fokker-Planck and Smoluchowski Equations -- 2.3 Interacting Particles, Liouville's Equation and Reduced Descriptions -- 3 Simple and Reinforced Random Walks in Space -- 3.1 The Pearson Random Walk -- 3.2 The General Evolution Equation for Space-Jump or Kangaroo Processes -- 3.3 The Evolution of Spatial Moments for General Kernels -- 3.4 The Effects of Long Waits or Large Jumps -- 3.5 Biased Jumps Dependent on Gradients or Internal Dynamics -- 3.6 Aggregation in Reinforced Random Walks -- 4 Velocity Jump Processes and Taxis Equations -- 4.1 The General Velocity-Jump Process -- 4.2 The Telegraph Process -- 4.3 Reduction of the VJ Process to a Diffusion Process -- 4.4 The Role of Internal Dynamics -- 4.5 Macroscopic Descriptions of Eukaryotic Cell Movement -- 5 Discussion -- References -- Hybrid Modelling of Individual Movement and Collective Behaviour -- 1 Introduction -- 2 Continuum vs. Agent-Based Models -- 2.1 Agent-Based Modelling -- 3 Hybrid Modelling: Theoretical Framework -- 3.1 A Position-Based Hybrid Model -- 3.2 Initial and Boundary Conditions -- 4 Hybrid Modelling: Numerical Implementation -- 4.1 Spatial Matching in Numerical Simulations -- 4.2 Other Aspects of Numerical Simulations -- 5 Case Study: Hybrid Modelling of Chemotaxis -- 5.1 The Keller-Segel Model. , 5.2 Hybrid Models of Chemotaxis -- 5.3 Analysis of the Dropout -- 6 Discussion -- References -- From Individual Movement Rules to Population Level Patterns: The Case of Central-Place Foragers -- 1 Introduction -- 2 Model Derivation -- 2.1 Population Dynamics -- 2.2 Individual Movement -- 2.2.1 Resource-Dependent Settling -- 2.2.2 Time-Dependent Settling -- 2.2.3 Prospect-Dependent Settling -- 2.2.4 Nondimensionalization -- 3 Effects of Movement Rules on Persistence -- 4 Effects of Movement Rules on Stability -- 4.1 Resource-Dependent Settling -- 4.2 Time-Dependent Settling -- 4.3 Prospect-Dependent Settling -- 5 Discussion -- References -- Transport and Anisotropic Diffusion Models for Movement in Oriented Habitats -- 1 Introduction -- 1.1 Biological Motivation -- 1.2 Mathematical Modelling -- 2 Transport Equations -- 2.1 Movement in an Oriented Environment -- 2.2 Environmental Distributions -- 3 The Parabolic Scaling -- 3.1 Motivation of the Parabolic Limit -- 3.2 Parabolic Limit in an Oriented Landscape -- 4 The Hyperbolic Scaling -- 5 The Moment Approach -- 5.1 Moment Closure -- 5.2 Fast Flux Relaxation -- 6 Comparison Between Scalings -- 6.1 Relationships Between Limit Equations -- 6.2 Assumptions Behind Limit Equations -- 7 Examples and Applications -- 7.1 Bidirectional and Nondirectional Environments -- 7.1.1 Isotropic Diffusion: The Pearson Walk -- 7.1.2 Anisotropic Diffusion Example -- 7.1.3 Steady States -- 7.1.4 Application to Seismic Line Following -- 7.2 Unidirectional Environments -- 7.2.1 Anisotropic Diffusion-Drift Example -- 7.2.2 Relation to Haptotaxis and Chemotaxis -- 7.3 Singular Distributions -- 7.3.1 Strictly Bidirectional: Degenerate Diffusion -- 7.3.2 Strictly Unidirectional: Relation to ODEs -- 7.4 Life in a Stream -- 8 Discussion -- 9 Moments of von Mises Distributions -- 9.1 Unimodal von Mises Distribution. , 9.2 Bimodal von Mises Distribution -- 10 Numerical Methods -- 10.1 Simulations of Transport Model -- 10.2 Simulations of Macroscopic Models -- References -- Incorporating Complex Foraging of Zooplankton in Models: Role of Micro- and Mesoscale Processes in Macroscale Patterns -- 1 Introduction -- 2 The Lagrangian vs. the Eulerian Approach in the Modelling of Zooplankton Dynamics -- 3 Modelling and Scaling the Zooplankton Functional Response -- 3.1 Defining the Zooplankton Functional Response in Real Ecosystems -- 3.2 Emergence of a Sigmoid (Holling Type III) Overall Zooplankton Functional Response -- 4 The Role of Intra-population Variability of Zooplankton in Population Persistence -- 4.1 Describing the Intra-population Variability of Zooplankton Grazers -- 4.2 Analysis of the Model of the Intra-population Variability of Zooplankton -- 5 Discussion and Conclusions -- Appendix 1 -- Appendix 2 -- References -- Part III Populations, Communities and Ecosystems -- Life on the Move: Modeling the Effects of Climate-Driven Range Shifts with Integrodifference Equations -- 1 Introduction -- 2 Is Further Better? -- 3 The Critical Range-Shift Speed -- 4 Numerical Approaches -- 5 Analytic Approximations -- 6 A Simple Example -- 7 A Simplifying Approximation -- 8 Realistic Kernels -- 8.1 Gaussian Distribution -- 8.2 Laplace Distribution -- 8.3 Cauchy Distribution -- 8.4 Modified Bessel Distribution -- 9 Discussion -- References -- Control of Competitive Bioinvasion -- 1 Introduction -- 2 A Competition-Diffusion Model with Annual Cycles and Random Extreme Events -- 2.1 Existence and Stability Ranges of Spatially Uniform Stationary Solutions -- 2.2 Annual Cycles of Growth, Harvesting and Diffusion -- 2.3 Random Extreme Events and Assisted Long-Distance Transport -- 2.4 Numerical Simulations I -- 3 A Competition-Diffusion Model with Infected Invader. , 3.1 Local Dynamics with Infection -- 3.2 Spatiotemporal Dynamics with Infection -- 3.3 Numerical Simulations II -- 4 Concluding Remarks -- References -- Destruction and Diversity: Effects of Habitat Loss on Ecological Communities -- 1 Introduction -- 2 The Ecological Model -- 2.1 The Single-Species Model -- 2.2 Two Independent Populations -- 2.3 Competition: Two Competing Species -- 2.4 Competition: More Than Two Competing Species -- 2.5 Predation -- 2.6 Food Chains -- 2.7 Mutualism -- 2.8 A Simple Food Web -- 2.9 Heterogeneity -- 3 Discussion -- References -- Emergence and Propagation of Patterns in Nonlocal Reaction-Diffusion Equations Arising in the Theory of Speciation -- 1 Speciation Theory and Nonlocal Reaction-Diffusion Equations -- 2 Spectrum of the Operator Linearized about a Stationary Solution -- 2.1 Equation (3) -- 2.2 Equation (4) -- 2.3 Essential Spectrum of the Operator Linearized about a Wave -- 3 Nonlinear Stability -- 3.1 An Abstract Theorem on Stability of Stationary Solutions -- 3.2 Stability of the Homogeneous Solution -- 3.3 Stability of Waves -- 3.4 Numerical Examples -- 4 Discussion -- References -- Numerical Study of Pest Population Size at Various Diffusion Rates -- 1 Introduction -- 1.1 Spatial Heterogeneity and the Effect of Diffusion -- 1.2 Goals and the Road Map -- 2 Numerical Integration on Coarse Grids: The Problem Outline -- 2.1 The Method -- 3 Simulation Data -- 3.1 Estimating Pest Population Size on Coarse Grids: Numerical Test Cases -- 4 The Impact of the Diffusion Rates on the Accuracy of Numerical Integration -- 4.1 Uniform Grid -- 4.2 The Analysis of the Grid Step Size for Ecological Distributions -- 4.3 Arbitrary Location of the Peak on a Uniform Coarse Grid -- 5 Nonuniform Grid -- 6 Discussion and Conclusions -- References -- LECTURE NOTES IN MATHEMATICS.
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  • 2
    Online Resource
    Online Resource
    Milton :CRC Press LLC,
    Keywords: Biological invasions -- Mathematical models. ; Electronic books.
    Description / Table of Contents: Exactly Solvable Models of Biological Invasion demonstrates the advantages and methods of obtaining exact solutions of the equations that describe nonlinear problems encountered in the study of invasive species spread. The authors present a comprehensive collection of exactly solvable models and a unified, self-contained description of the relevant mathematical methods. They also provide new insight into important issues such as the impact of the Allee effect and the impact of predation. Full calculation details make this presentation accessible to biologists as well as applied mathematicians, and a range of ecological examples and applications demonstrate the utility of exact methods in practice.
    Type of Medium: Online Resource
    Pages: 1 online resource (232 pages)
    Edition: 1st ed.
    ISBN: 9781420034967
    Series Statement: Chapman and Hall/CRC Mathematical Biology Series
    DDC: 577.18015118
    Language: English
    Note: Cover -- Title -- Copyright -- Preface -- Contents -- List of Figures -- Chapter 1: Introduction -- Chapter 2: Models of biological invasion -- Chapter 3: Basic methods and relevant examples -- Chapter 4: Single-species models -- Chapter 5: Density-dependent diffusion -- Chapter 6: Models of interacting populations -- Chapter 7: Some alternative and complementary approaches -- Chapter 8: Ecological examples and applications -- Chapter 9: Appendix: Basic background mathematics -- References -- Index.
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  • 3
    Keywords: Ecology-Mathematical models. ; Epidemiology-Mathematical models. ; Electronic books.
    Description / Table of Contents: Reviewing the significant progress made in understanding spatiotemporal patterning in ecological and epidemiological systems, this resource shows that mathematical modeling and numerical simulations are effective tools in the study of population ecology and epidemiology. It takes a unified approach to population dynamics and epidemiology by present.
    Type of Medium: Online Resource
    Pages: 1 online resource (470 pages)
    Edition: 1st ed.
    ISBN: 9781482286137
    Series Statement: Chapman and Hall/CRC Mathematical Biology Series
    DDC: 577.015118
    Language: English
    Note: Cover -- Half Title -- Title Page -- Copyright Page -- Original Title Page -- Dedication Page -- Supplementary Resources Disclaimer -- Preface -- Table of Contents -- I Introduction -- 1 Ecological patterns in time and space -- 1.1 Local structures -- 1.2 Spatial and spatiotemporal structures -- 2 An overview of modeling approaches -- II Models of temporal dynamics -- 3 Classical one population models -- 3.1 Isolated populations models -- 3.1.1 Scaling -- 3.2 Migration models -- 3.2.1 Harvesting -- 3.3 Glance at discrete models -- 3.4 Peek into chaos -- 4 Interacting populations -- 4.1 Two-species prey-predator population model -- 4.2 Classical Lotka-Volterra model -- 4.2.1 More on prey-predator models -- 4.2.2 Scaling -- 4.3 Other types of population communities -- 4.3.1 Competing populations -- 4.3.2 Symbiotic populations -- 4.3.3 Leslie-Gower model -- 4.3.4 Classical Holling-Tanner model -- 4.3.5 Other growth models -- 4.3.6 Models with prey switching -- 4.4 Global stability -- 4.4.1 General quadratic prey-predator system -- 4.4.2 Mathematical tools for analyzing limit cycles -- 4.4.3 Routh-Hurwitz conditions -- 4.4.4 Criterion for Hopf bifurcation -- 4.4.5 Instructive example -- 4.4.6 Poincaré map -- 4.5 Food web -- 4.6 More about chaos -- 4.7 Age-dependent populations -- 4.7.1 Prey-predator, age-dependent populations -- 4.7.2 More about age-dependent populations -- 4.7.3 Simulations and brief discussion -- 5 Case study: biological pest control in vineyards -- 5.1 First model -- 5.1.1 Modeling the human activity -- 5.2 More sophisticated model -- 5.2.1 Models comparison -- 5.3 Modeling the ballooning effect -- 5.3.1 Spraying effects and human intervention -- 5.3.2 Ecological discussion -- 6 Epidemic models -- 6.1 Basic epidemic models -- 6.1.1 Simplest models -- 6.1.2 Standard incidence -- 6.2 Other classical epidemic models. , 6.3 Age- and stage-dependent epidemic system -- 6.4 Case study: Aujeszky disease -- 6.5 Analysis of a disease with two states -- 7 Ecoepidemic systems -- 7.1 Prey-diseased-predator interactions -- 7.1.1 Some biological considerations -- 7.2 Predator-diseased-prey interactions -- 7.3 Diseased competing species models -- 7.3.1 Simulation discussion -- 7.4 Ecoepidemics models of symbiotic communities -- 7.4.1 Disease effects on the symbiotic system -- 7.4.2 Disease control by use of a symbiotic species -- III Spatiotemporal dynamics and pattern formation: deterministic approach -- 8 Spatial aspect: diffusion as a paradigm -- 9 Instabilities and dissipative structures -- 9.1 Turing patterns -- 9.1.1 Turing patterns in a multispecies system -- 9.2 Differential flow instability -- 9.3 Ecological example: semiarid vegetation patterns -- 9.3.1 Pattern formation due to nonlocal interactions -- 9.4 Concluding remarks -- 10 Patterns in the wake of invasion -- 10.1 Invasion in a prey-predator system -- 10.2 Dynamical stabilization of an unstable equilibrium -- 10.2.1 A bifurcation approach -- 10.2.2 Comparison of wave speeds -- 10.3 Patterns in a competing species community -- 10.4 Concluding remarks -- 11 Biological turbulence -- 11.1 Self-organized patchiness and the wave of chaos -- 11.1.1 Stability diagram and the hierarchy of regimes -- 11.1.2 Patchiness in a two-dimensional case -- 11.2 Spatial structure and spatial correlations -- 11.2.1 Intrinsic lengths and scaling -- 11.3 Ecological implications -- 11.3.1 Plankton patchiness on a biological scale -- 11.3.2 Self-organized patchiness, desynchronization, and the paradox of enrichment -- 11.4 Concluding remarks -- 12 Patchy invasion -- 12.1 Allee effect, biological control, and one-dimensional patterns of species invasion -- 12.1.1 Patterns of species spread. , 12.2 Invasion and control in the two-dimensional case -- 12.2.1 Properties of the patchy invasion -- 12.3 Biological control through infectious diseases -- 12.3.1 Patchy spread in SIR model -- 12.4 Concluding remarks -- IV Spatiotemporal patterns and noise -- 13 Generic model of stochastic population dynamics -- 14 Noise-induced pattern transitions -- 14.1 Transitions in a patchy environment -- 14.1.1 No noise -- 14.1.2 Noise-induced pattern transition -- 14.2 Transitions in a uniform environment -- 14.2.1 Standing waves driven by noise -- 15 Epidemic spread in a stochastic environment -- 15.1 Model -- 15.2 Strange periodic attractors in the lytic regime -- 15.3 Local dynamics in the lysogenic regime -- 15.4 Deterministic and stochastic spatial dynamics -- 15.5 Local dynamics with deterministic switch from lysogeny to lysis -- 15.6 Spatiotemporal dynamics with switches from lysogeny to lysis -- 15.6.1 Deterministic switching from lysogeny to lysis -- 15.6.2 Stochastic switching -- 16 Noise-induced pattern formation -- References -- Index.
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  • 4
    Publication Date: 2022-06-27
    Description: © The Author(s), (2022). This article is distributed under the terms of the Creative Commons Attribution License. The definitive version was published in Ahmed, D. A., Hudgins, E. J., Cuthbert, R. N., Kourantidou, M., Diagne, C., Haubrock, P. J., Leung, B., Liu, C., Leroy, B., Petrovskii, S., Beidas, A., & Courchamp, F. Managing biological invasions: the cost of inaction. Biological Invasions. (2022), https://doi.org/10.1007/s10530-022-02755-0.
    Description: Ecological and socioeconomic impacts from biological invasions are rapidly escalating worldwide. While effective management underpins impact mitigation, such actions are often delayed, insufficient or entirely absent. Presently, management delays emanate from a lack of monetary rationale to invest at early invasion stages, which precludes effective prevention and eradication. Here, we provide such rationale by developing a conceptual model to quantify the cost of inaction, i.e., the additional expenditure due to delayed management, under varying time delays and management efficiencies. Further, we apply the model to management and damage cost data from a relatively data-rich genus (Aedes mosquitoes). Our model demonstrates that rapid management interventions following invasion drastically minimise costs. We also identify key points in time that differentiate among scenarios of timely, delayed and severely delayed management intervention. Any management action during the severely delayed phase results in substantial losses (〉50% of the potential maximum loss). For Aedes spp., we estimate that the existing management delay of 55 years led to an additional total cost of approximately $ 4.57 billion (14% of the maximum cost), compared to a scenario with management action only seven years prior (〈 1% of the maximum cost). Moreover, we estimate that in the absence of management action, long-term losses would have accumulated to US$ 32.31 billion, or more than seven times the observed inaction cost. These results highlight the need for more timely management of invasive alien species—either pre-invasion, or as soon as possible after detection—by demonstrating how early investments rapidly reduce long-term economic impacts.
    Description: The authors acknowledge the French National Research Agency (ANR-14-CE02-0021) and the BNP-Paribas Foundation Climate Initiative for funding the InvaCost project that allowed the construction of the InvaCost database. The present work was conducted following a workshop funded by the AXA Research Fund Chair of Invasion Biology and is part of the AlienScenarios project funded by BiodivERsA and Belmont-Forum call 2018 on biodiversity scenarios. DAA is funded by the Kuwait Foundation for the Advancement of Sciences (KFAS), grant no. PR1914SM-01 and the Gulf University for Science and Technology (GUST) internal seed fund, grant no. 234597. EJH is supported by a Fonds de recherche du Québec—nature et téchnologies B3X fellowship. RNC acknowledges funding from the Alexander von Humboldt Foundation. CL was sponsored by the PRIME programme of the German Academic Exchange Service (DAAD) with funds from the German Federal Ministry of Education and Research (BMBF).
    Keywords: InvaCost ; Invasive alien species ; Logistic growth ; Socioeconomic impacts ; Prevention and biosecurity ; Long-term management
    Repository Name: Woods Hole Open Access Server
    Type: Article
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  • 5
    Publication Date: 2024-02-07
    Description: Ecological and socioeconomic impacts from biological invasions are rapidly escalating worldwide. While effective management underpins impact mitigation, such actions are often delayed, insufficient or entirely absent. Presently, management delays emanate from a lack of monetary rationale to invest at early invasion stages, which precludes effective prevention and eradication. Here, we provide such rationale by developing a conceptual model to quantify the cost of inaction, i.e., the additional expenditure due to delayed management, under varying time delays and management efficiencies. Further, we apply the model to management and damage cost data from a relatively data-rich genus (Aedes mosquitoes). Our model demonstrates that rapid management interventions following invasion drastically minimise costs. We also identify key points in time that differentiate among scenarios of timely, delayed and severely delayed management intervention. Any management action during the severely delayed phase results in substantial losses (〉50% of the potential maximum loss). For Aedes spp., we estimate that the existing management delay of 55 years led to an additional total cost of approximately $ 4.57 billion (14% of the maximum cost), compared to a scenario with management action only seven years prior (〈 1% of the maximum cost). Moreover, we estimate that in the absence of management action, long-term losses would have accumulated to US$ 32.31 billion, or more than seven times the observed inaction cost. These results highlight the need for more timely management of invasive alien species—either pre-invasion, or as soon as possible after detection—by demonstrating how early investments rapidly reduce long-term economic impacts.
    Type: Article , PeerReviewed
    Format: text
    Format: text
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