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Spatial Structure & Metapopulations. Clematis fremontii Erickson 1945.

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Presentation on theme: "Spatial Structure & Metapopulations. Clematis fremontii Erickson 1945."— Presentation transcript:

1 Spatial Structure & Metapopulations

2 Clematis fremontii Erickson 1945

3 Dispersion of Individuals within Populations Dispersion of individuals within a population describes their spacing with respect to one another. A variety of patterns is possible: –clumped (individuals in discrete groups) –evenly spaced (each individual maintains a minimum distance from other individuals) –random (individuals distributed independently of others within a homogeneous area)

4 Desert shrubs can be nearly regular in distribution

5 Aspen in the Rocky Mountains are clonal

6 Causes of Dispersion Even spacing may arise from direct interactions among individuals: –maintenance of minimum distance between individuals or direct competition for limited resources may cause this pattern Clumped distribution may arise from: –social predisposition to form groups –clumped distribution of resources –tendency of progeny to remain near parent Spatial pattern is scale-dependent

7 Clematis fremontii Erickson 1945

8 Populations exist in heterogeneous landscapes. Uniform habitats are the exception rather than the rule: –most populations are divided into subpopulations living in suitable habitat patches Degree to which members of subpopulations are isolated from one another depends on: –distances between subpopulations –nature of intervening environment –mobility of the species

9 Metapopulation Model The metapopulation model views a population as a set of subpopulations occupying patches of a particular habitat: –intervening habitat is referred to as the habitat matrix: –the matrix is viewed only as a barrier to movement of individuals between subpopulations

10 Metapopulation models: applications in conservation planning and management. As natural populations become increasingly fragmented by human activities, ecologists have turned increasingly to the metapopulation concept. Two kinds of processes contribute to dynamics of metapopulations: –growth and regulation of subpopulations within patches –colonization to form new subpopulations and extinction of existing subpopulations

11 Southern California Spotted Owl

12 Connectivity determines metapopulation dynamics When individuals move frequently between subpopulations, local fluctuations are damped out. At intermediate levels of movement: –the metapopulation behaves as a shifting mosaic of occupied and unoccupied patches At low levels of movement: –the subpopulations behave independently –as small subpopulations go extinct, they cannot be reestablished, and the entire population eventually goes extinct

13 Local extinction Regional extinction is the probability that the population goes extinct. Local extinction is the probability that the part of the population in an occupied patch does extinct = p e Probability of persistence for n years = probability of no extinction for n years in a row = (1-p e ) n p e =.7, n = 5, survival =.00243

14 Regional persistence Consider x independent patches Probability of persistence in one patch = 1 - p e Probability of persistence in at least one patch is one minus probability they are all extinct = 1 – p e x p e =.7, t = 10 patches, survival =.97

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16 The metapopoulation model f = fraction of sites occupied (0-1) I = Immigration rate (or colonization rate) E = Local extinction rate df/dt = I-E

17 Probability of local colonization Physical conditions Biological conditions (preditors, pathogens, competitors) Patch size Patch isolation Proximity to occupied patches I = p i (1-f)

18 Basic model Extinction rate is the product of probability local extinction rate times the fraction of sites occupied = p e f Extinction rate is 0 if p e or f is 0 df/dt = p i (1-f) –p e f The simplest model

19 Assumptions to relax? Homogeneous patches (size, isolation, quality, resource levels, etc) No spatial structure (no neighborhoods) No time lags (instantaneous response) Constant p e and p i Relationships can exist between regional occurrence and local colonization and extinction Large number of patches (no demographic stochasticity)

20 Island model Probability of immigration is fixed. Propagule rain fixed by a constant, large source population. df/dt = p i (1-f)-p e f df/dt = 0  p i - p i f –p e f = 0 f = p i / (p i +p e ) [always positive]

21 Internal colonization Only source of propagules is occupied patches P i = if where i is a measure of how much each occupied site will contribute to colonization. df/df = if(1-f)-p e f f = 1-(p e /i)

22 Rescue effect Probability of extinction can be influenced by immigration from occupied patches P e = e(1-f) where e is a measure of the strength of the rescue effect If f = 1, p e = 0, which is unrealistic df/dt = p i (1-f) –ef(1-f) f = p i /e Persistence if p i >0 with rescue effect, and if e<p i then patches are saturated.

23 Internal colonization & rescue Df/dt = if(1-f) - ef(1-f) If i > e, population will grow to f=1 If e > 1, population will decrease to f=0

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25 Connectivity determines metapopulation dynamics. When individuals move frequently between subpopulations, local fluctuations are damped out. At intermediate levels of movement: –the metapopulation behaves as a shifting mosaic of occupied and unoccupied patches At low levels of movement: –the subpopulations behave independently –as small subpopulations go extinct, they cannot be reestablished, and the entire population eventually goes extinct

26 Source-Sink Model & Mass effect Model The source-sink model recognizes differences in quality of suitable habitat patches: –in source patches, where resources are abundant: individuals produce more offspring than needed to replace themselves surplus offspring disperse to other patches –in sink patches, where resources are scarce: populations are maintained by immigration of individuals from elsewhere

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30 Landscape Model The landscape model considers effects of differences in habitat quality within the habitat matrix: –the quality of a habitat patch can be affected by the nature of the surrounding matrix quality is enhanced by presence of resources, such as nesting materials or pollinators quality is reduced by presence of predators or disease organisms –some matrix habitats are more easily traversed than others


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