Lecture 10: Biodiversity and Biogeography

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UN definition of Biodiversity

  • Total number of species on Earth (global species richness)

  • Evolutionary diversity represented by these species

  • Diverse communities and ecosystems these species build

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How does the equilibrium theory of island biogeography apply to island-like habitats such as mountains?

  • Island-like habitats (e.g., mountains) function like ecological “islands” because they are isolated patches of suitable habitat surrounded by unsuitable areas.

  • Species richness on these habitats is determined by the same balance of immigration (species arriving from other patches) and extinction (species lost within the patch).

  • Closer, larger, or more connected mountain habitats have higher immigration and lower extinction rates, while smaller or more isolated ones support fewer species—mirroring the classic island biogeography model.

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About 2 million species have been described in the scientific literature. But there are biases

  • We know there are 1000000 species of insects but they are more studied because

    • They are easier to sample and there are lots of them as a result scientists are very confident we have identified 50% of insects that exist

  • Fungi are unstudied and we have barely described 5% of fungi

  • Bacteria that harms us is well studied, but bacteria that for example just exists in the soil and is not virus, is not as studied

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The Challenges of Estimating Global Species Richness

  • A historical reliance on physical and morphological characteristics

  • Biases exist with respect to which species / ecosystem are studied.

  • Many species are hard to find and researchers are limited by logistic, time, and funding constraints.

  • Many species are going extinct before they are described.

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A historical reliance on physical and morphological characteristics

  • Linneus was the first to do this in the 17th century

  • Darwin came later and spoke on evolution

  • But both these scientists knew nothing about DNA or they lacked the tools to examine it

  • This often led to morphs of a single species being described as separate species.

    • “These things look really different so they are different species “

  • Ex. These 2 birds do not interbreed, but they look to be part of the same species when in reality they are not

<ul><li><p>Linneus was the first to do this in the 17th century</p></li><li><p>Darwin came later and spoke on evolution</p></li><li><p>But both these scientists knew nothing about DNA or they lacked the tools to examine it</p></li><li><p>This often led to morphs of a single species being described as separate species.</p><ul><li><p>“These things look really different so they are different species “</p></li></ul></li><li><p>Ex. These 2 birds do not interbreed, but they look to be part of the same species when in reality they are not</p></li></ul><p></p>
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Biases exist with respect to which species are studied.

  • Every scientists gets to decide what is interesting to them

  • This impacts what gets studied and what doesn't get studied

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Biases exist with respect to which ecosystems are studied.

  • Deep sea requires expensive equipment and certain skills that maybe not everyone has.

  • Rainforest is more convenient to study because you can just walk around and observe with no equipment needed to start

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Many species are hard to find and researchers are limited by logistic, time, and funding constraints

In a big forest, there are so many things hiding that will not catch our attention → not studied as well as big noticeable or flashy species

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Many species are going extinct before they are described.

  • Usually because of human activity

    • Hunted to extinction

    • Loss of habitat because of deforestation

  • Reminds us of mass extinction when meteor hit earth, changed the climate, so dinosaurs went extinct

  • We are in the middle of 6th mass extinction in recent history of this planet. Due to anthropogenic influences, a recent study found that 48% of species have a declining population and only 3% have increasing populations. 33% of species currently classified as non-threatened are declining

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Determining Species Richness & Community Composition

  • Determining which species are present in a community can be challenging; recording all species in a community is typically impossible

  • Sampling techniques for determining community composition are similar to those discussed in Lecture 4 for populations, such as sampling plots, line transects, and camera traps.

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Species-Abundance Relationships

  • Sample A: equal chance that I will encounter all of the species in a short period of time

  • Species B: might not encounter the blue butterfly because there are so many yellow and not as many of the other species

  • So how do we say this community consists of all 5 species in both samples, if in B it is unlikely that I sample everyone

  • Rarity imposes challenges for sampling, as rare species are rarely sampled and may, thus, be missed when documenting community composition

<ul><li><p>Sample A: equal chance that I will encounter all of the species in a short period of time</p></li><li><p>Species B: might not encounter the blue butterfly because there are so many yellow and not as many of the other species</p></li><li><p>So how do we say this community consists of all 5 species in both samples, if in B it is unlikely that I sample everyone</p></li><li><p>Rarity imposes challenges for sampling, as rare species are rarely sampled and may, thus, be missed when documenting community composition</p></li></ul><p></p>
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In most communities,

  • a few species account for most individuals; most species can be considered rare.

  • The struggle is with the rare species: I will find a common butterfly, but will I also find a rare one

<ul><li><p>a few species account for most individuals; most species can be considered rare.</p></li><li><p>The struggle is with the rare species: I will find a common butterfly, but will I also find a rare one</p></li></ul><p></p>
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Rarity imposes substantial challenges on sampling

  • Efforts are limited by time, logistic, and financial constraints, so researchers need to determine how much sampling effort to expend in a given area.

  • Given that we cannot sample every individual in a community, and given that we do not know the true state of a community, how do we know when our sampling efforts have captured a community’s species richness and composition adequately

    • Species accumulation curves

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Species accumulation curves

  • describe how the number of species that were identified increases with the number of individuals sampled.

  • They are initially steep but then level off once most species have been identified (the more you sample, the less likely it is that you see something new).

  • Levelling off of the species accumulation curve can indicate adequate representation of the community in the samples.→ confidence you have sampled everything, nothing new left to find

<ul><li><p>describe how the number of species that were identified increases with the number of individuals sampled.</p></li><li><p>They are initially steep but then level off once most species have been identified (the more you sample, the less likely it is that you see something new).</p></li><li><p>Levelling off of the species accumulation curve can indicate adequate representation of the community in the samples.→ confidence you have sampled everything, nothing new left to find</p></li></ul><p></p>
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Species-Area Relationships

Similarly to how we are unable to sample every individual in a community, we are also unable to sample every area of an ecosystem.

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Hierarchical sampling designs

collecting data at multiple spatial scales at randomly chosen locations allows understanding how community composition might vary across different areas.

<p><span><span>collecting data at multiple spatial scales at randomly chosen locations allows understanding how community composition might vary across different areas.</span></span></p>
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Species-area relationships suggest that the number of species that are found will

increase with the area that is sampled: steeply first, and then more slowly as the probability increases that sampled species have already been observed in previous areas

<p><span><span>increase with the area that is sampled: steeply first, and then more slowly as the probability increases that sampled species have already been observed in previous areas</span></span></p>
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Species-area relationships can typically be described using a power function

  • S = cA^z

  • or equivalently, its log-log transformation log S = log c + z log A

  • where

    • A = area

    • S = number of species in the area

    • c = avg. number of species per unit area

    • z = slope of log-log transformed species- area relationship (informing on how quickly new species are accumulated when new areas are added)

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Log-log transformation of power function causes

  • Linear relationships between the log of the area and the log of the species

  • This linear relationships allow you to estimate slope (z) and intercept (c)

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<p><span><span>Which of these communities would you consider to be more diverse?</span></span></p>

Which of these communities would you consider to be more diverse?

  • Both are equally diverse because both have 4 species

  • species richness is four in both communities, but community B is considered more diverse because of a higher species evenness.

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Two communities may have the same species richness (the number of species in a community), but differ in their composition.

Enter species evenness

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Species evenness

describes how evenly individuals are spread among species by considering the relative abundances of each species compared to one another.

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species richness

the number of species in a community

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The Shannon-Wiener Diversity Index (ON THE EXAM, DO AN EXAMPLE FROM TEXTBOOK)

  • is a commonly used summary metric for species diversity.

  • It incorporates both species richness and species evenness.

  • S = number of species in the community

  • pi = proportion of individuals that belong to the ith species

<ul><li><p>is a commonly used summary metric for species diversity.</p></li><li><p>It incorporates both species richness and species evenness.</p></li><li><p>S = number of species in the community</p></li><li><p>pi = proportion of individuals that belong to the ith species</p></li></ul><p></p>
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Properties of the Shannon-Wiener Diversity index:

  • For a community that contains exactly one species, H=0.

  • For a fixed species richness (S), increasing evenness increases H.

  • For a fixed evenness (e.g., pi = 1/S for all species i), increasing species richness (S) increases H.

  • A higher H indicates a higher diversity, accounting for both richness and evenness.

  • A higher H indicates a higher diversity, but it does not inform on whether this is because of high richness or evenness.

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The Shannon-Wiener Diversity Index can indicate which

communities are more diverse than others (higher H).

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Rank abundance curves

  • which plot the proportional abundance of each species (pi) relative to the others in rank order

  • can be used to understand whether differences in diversity are due to differences in species richness, evenness, or both.(useful because we can’t just tell from the Shannon-Wiener Diversity Index Value)

<ul><li><p>which plot the proportional abundance of each species (pi) relative to the others in rank order</p></li><li><p>can be used to understand whether differences in diversity are due to differences in species richness, evenness, or both.(useful because we can’t just tell from the Shannon-Wiener Diversity Index Value)</p></li></ul><p></p>
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The length of a rank abundance curve indicates

species richness

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steepness of a rank abundance curve indicates

evenness

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Shallower slope on rank abundance curve means species is

More even

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Longer line on abundance curve means

There are more species (increased species richness)

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Summary metrics, such as the Shannon-Wiener Diversity Index, can be useful for summarizing and comparing key characteristics of communities.

  • However, two communities could have identical species richness and evenness but completely different species compositions and functions

  • It matters which species are present in a community; simply tallying up species richness / evenness might miss key details

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Seven Forms of Rarity

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Phylogenetic trees

graphically depict the evolutionary relationships among a set of species.

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The length of branches on phylogenetic trees typically represent

  • the time since evolutionary divergence from the previous node

  • Loosing something with longer evolutionary history is more significant than newer species with shorter branches

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Phylogenetic diversity (PD)

can be measured by adding up all branch lengths within a phylogeny to create a single number that can be compared across locations and through time.

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A set of species that are evolutionarily very different from one another will have a higher or lower PD score that a set of closely related species

Higher

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Evaluating experimental data on the thermal sensitivity of the development of helminths (parasitic worms) for 87 species revealed

  • that thermal sensitivities were systematically influenced by phylogenetic relationships: related species tended to have similar thermal sensitivities, indicating that some helminth taxa are inherently more affected by rising temperatures than others

  • Using phylogeny allows us to make conclusions

    • Instead of saying “species x is temp sensitive” we can say “species x and all its relatives are temp sensitive” regardless of whether or not we have studied them

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Human-linked prehistoric extinctions

  • resulted in a loss of two billion years of evolutionary history among mammals; an additional loss of another 500 million years of evolutionary history is expected through recent extinctions.

  • Example: Past and expected future losses of phylogenetic diversity in mammals through extinctions

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Functional traits

  • are characteristics of species that describe their ecological roles in a community.

  • Example: Functional traits of plants are often defined based on their morphology (e.g., woodiness, leaf characteristics, height) and on how they contribute to forest canopy structure

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Functional diversity dendrograms

  • graphically depict the relationships among a set of species in terms of their functional traits.

  • Adding up the length of all branches produces a metric that can be regarded as an estimate of a community’s functional diversity (FD), as measured through functional richness (the number of traits present in a community) and functional evenness (the proportion of individuals in each functional group

  • Ex. Loosing all of A, B, C, D, E is worse than if I lost D, H, and K, because there are still other species that exist with those functions

<ul><li><p>graphically depict the relationships among a set of species in terms of their functional traits.</p></li><li><p>Adding up the length of all branches produces a metric that can be regarded as an estimate of a community’s functional diversity (FD), as measured through functional richness (the number of traits present in a community) and functional evenness (the proportion of individuals in each functional group</p></li><li><p>Ex. Loosing all of A, B, C, D, E is worse than if I lost D, H, and K, because there are still other species that exist with those functions</p></li></ul><p></p>
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Species richness and other metrics may vary across habitats within an ecosystem, with

heterogeneous habitats holding more species than homogeneous habitats.

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Species richness across different habitats can be described using

α-, β-, and γ-diversity

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γ-diversity:

  • species richness across a region made up of smaller localities

  • Across the entire region

  • It is the total number of species found across all habitats combined.

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α-diversity:

  • the average number of species found within small, local-scale habitats in a region

  • Within a habitat

  • It is the average number of species in a single local site.

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β-diversity:

a measure of heterogeneity of community composition among localities. β-diversity can be defined in many ways; one of the most common definitions is β = γ / α

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Two Ways to Get High γ-Diversity

  1. High α-diversity (many species within each habitat)

    • Habitats are similar to each other but each contains lots of species.

    • β-diversity is low because there is little turnover between habitats.

  2. High β-diversity (big differences between habitats)

    • Habitats contain different sets of species.

    • Even if α is low, high species turnover produces a high γ.

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term image
  • Example 1 (Top Image: Empire Islands)

    • γ = 7 species total

    • Habitats are very similar (lots of overlap).

    • α = 6, meaning habitats have many species each.

    • β = γ / α = 7 / 6 = 1.17 → low turnover

    • High γ comes mostly from high α, not β.

  • Example 2 (Bottom Image: Alliance Islands)

    • γ = 12 species total

    • No overlap between habitats (each has unique species).

    • α = 4 (few species per habitat).

    • β = γ / α = 12 / 4 = 3 → high turnover

    • High γ comes from high β-diversity, not α.

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Think – Pair – Share: Biodiversity Loss : why do i care about loosing species

biodiversity maintains ecosystem stability and human well-being. Species support essential services like pollination, nutrient cycling, water purification, and food production. Losing species reduces ecosystem resilience, threatens economies and human health, and results in irreversible loss of evolutionary history

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What hold the largest biodiversity among terrestrial biomes

Tropical rainforests

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What hold the largest biodiversity among aquatic zones

tropical coral reefs

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Trends in phylogenetic diversity tend to be similar to those in species richness.

More species near equator, and less species as you go further from equator

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Differences between the two (e.g., areas with comparatively low species richness but high phylogenetic diversity) can indicate

hotspots of evolutionary diversity (e.g., due to long and unique evolutionary histories).

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Many hypotheses have been proposed for explaining the observed latitudinal gradients in diversity, including differences between lower and higher latitudes in

  • (A) diversification rate

  • (B) diversification time

  • (C) primary productivity.

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Diversification Rate

Hypothesis 1: Species diversity is largest in the tropics because the tropics have a higher species diversification rate than higher-latitude areas: large, thermally stable areas result in larger population sizes and larger population ranges, which decreases each species’ extinction risk and increases the rates of speciation

<p><span><span>Hypothesis 1: Species diversity is largest in the tropics because the tropics have a higher species diversification rate than higher-latitude areas: large, thermally stable areas result in larger population sizes and larger population ranges, which decreases each species’ extinction risk and increases the rates of speciation</span></span></p>
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Diversification time

  • Hypothesis 2: Species diversity is larger in the tropics than in higher-latitude areas because the tropics have been climatically stable for longer periods of time, thus giving species more time to evolve.

  • In fact, it has been hypothesized that many species that are found elsewhere also originated in the tropics and then dispersed from there.

  • Last ice age in Canada was 10 000 yrs ago, but Brazil never had an ice age. So while Canada was covered in ice, Brazil was continuing in a thriving ecosystem where more variety of species could exist

<ul><li><p>Hypothesis 2: Species diversity is larger in the tropics than in higher-latitude areas because the tropics have been climatically stable for longer periods of time, thus giving species more time to evolve.</p></li><li><p>In fact, it has been hypothesized that many species that are found elsewhere also originated in the tropics and then dispersed from there.</p></li><li><p>Last ice age in Canada was 10 000 yrs ago, but Brazil never had an ice age. So while Canada was covered in ice, Brazil was continuing in a thriving ecosystem where more variety of species could exist</p></li></ul><p></p>
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Primary productivity

Hypothesis 3: Species diversity is larger in terrestrial tropical systems than in temperate ones, because terrestrial productivity is generally highest in the tropics: high productivity promotes higher carrying capacities and thus larger population sizes and decreased extinctions risks

<p><span><span>Hypothesis 3: Species diversity is larger in terrestrial tropical systems than in temperate ones, because terrestrial productivity is generally highest in the tropics: high productivity promotes higher carrying capacities and thus larger population sizes and decreased extinctions risks</span></span></p>
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<p><span><span>On which of these islands would you expect to find more species</span></span></p>

On which of these islands would you expect to find more species

B because islands that are close to mainland and large will have more species

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How does the size of an island correlates with the number of species it harbors.

  • Positively

  • Larger the island = more species you would find

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<p><span><span>On which of these islands would you expect to find more species?</span></span></p>

On which of these islands would you expect to find more species?

  • Right hand one because it is closer to the mainland

  • The closer an island is to the mainland, the higher the colonization rate, because species can disperse there more easily than to distant islands.

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How does the distance between an island and the mainland correlates with the island’s species richness

  • negatively

  • Farther an island is from mainland = less species

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The Equilibrium Theory of Island Biogeography

  • suggests that the number of species on an island depends on how immigration rates and extinction rates balance against one another.

  • No new species is created through evolutions of a species

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Rates of immigration:

  • The theory assumes that ecological timescales are much faster than evolutionary timescales, so that the rate of new species arrivals on an island is primarily driven by immigration from somewhere else, rather than by speciation on the island.

  • Species richness increases when a new species that is not present on the island arrives; the rate of increase at which new species arrive slows when the island’s species richness is high, as many arrivals are already present on the island

  • The remoteness of an island influences immigration rates: higher immigration rates for islands that are closer to a source of species, such as the mainland

<ul><li><p>The theory assumes that ecological timescales are much faster than evolutionary timescales, so that the rate of new species arrivals on an island is primarily driven by immigration from somewhere else, rather than by speciation on the island.</p></li><li><p>Species richness increases when a new species that is not present on the island arrives; the rate of increase at which new species arrive slows when the island’s species richness is high, as many arrivals are already present on the island</p></li><li><p>The remoteness of an island influences immigration rates: higher immigration rates for islands that are closer to a source of species, such as the mainland</p></li></ul><p></p>
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Rate of immigration is larger for

  • Islands with few species

  • Empty island because it doesn't matter who comes to the island, that species is new to island

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Rate of immigration smaller for

  • Island with already many species

  • already colonized islands because rate of increase at which new species arrive slows when the island’s species richness is high, as many arrivals are already present on the island

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Rates of extinction:

  • Higher species richness results in higher extinction rates because (a) more species can go extinct when more species are present; and (b) higher species richness leads to increased competition for limited resources, leading to smaller population sizes and higher extinction probabilities for each species.

  • Island size influences extinction rates: higher extinction rates for smaller islands because increased resource limitation leads to smaller population sizes and higher extinction probabilities for each species.

<ul><li><p>Higher species richness results in higher extinction rates because (a) more species can go extinct when more species are present; and (b) higher species richness leads to increased competition for limited resources, leading to smaller population sizes and higher extinction probabilities for each species.</p></li><li><p>Island size influences extinction rates: higher extinction rates for smaller islands because increased resource limitation leads to smaller population sizes and higher extinction probabilities for each species.</p></li></ul><p></p>
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Extinction rate increases

The more species you have

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Putting the 2 graphs together

  • The equilibrium number of species on an island occurs where immigration and extinction rates balance exactly.

    • Look at combinations (for example, colonization on near island that is large), look where two curves intersect = that gives me largest number of species

    • Small island on far : smaller species richness

  • The model predicts that species richness will be highest on large islands near to the mainland, and smallest on small islands far from the mainland

<ul><li><p>The equilibrium number of species on an island occurs where immigration and extinction rates balance exactly.</p><ul><li><p>Look at combinations (for example, colonization on near island that is large), look where two curves intersect = that gives me largest number of species</p></li><li><p>Small island on far : smaller species richness</p></li></ul></li><li><p>The model predicts that species richness will be highest on large islands near to the mainland, and smallest on small islands far from the mainland</p></li></ul><p></p>
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species richness will be highest on

large islands near to the mainland

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species richness will be smallest on

small islands far from the mainland

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Turnover rates are predicted to be largest on

small islands near the mainland

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Turnover rates are predicted to be smallest on

large islands far from the mainland

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Turnover rates

the rates at which newly colonizing species replace newly extinct species