ecology exam 3

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Arkansas state- mangan

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110 Terms

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extinction
loss of established species fro a patch; rate of extinction increases with number of species already established on patch; model assumes extinction is random,, therefore, if more species high chance species are lost
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number of species at equilibrium
species richness is stable, but species compositions might be changing
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turnover rate
rate at which a species is replacing the other
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structural connectivity
the physical arrangement of patches; isolated patches> low connectivity; higher connectivity> less isolates maybe connected
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corridor
area of similar habitat connecting patches (facilitates dispersal of organisms from one patch to another)
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edge species
boundary edges separating patches have distinct environmental conditions, and species that are adapted to specialize in edges
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landscape connectivity
the degree to which the landscape allows organisms to move from one patch to another
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The SIR Model
simple model that predicts how infections will move through the populaiton
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what does the SIR model stand for?
susceptible, infected, recovered
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infection
how quickly susceptible individuals become infected
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recovery
how quickly infected people recover
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what are the 3 determinants of disease spread?
population density, transmission rate, infectious period
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population density
number of individuals per unit area
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transmission rate
depends on rate of contact between infected and susceptible individuals that leads to new infection
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infectious period
the average period of time an infected person can transmit
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simple assumptions of disease spread

1. direct infection only
2. no evolution
3. does not consider new births or deaths
4. once recovered you can never get disease again
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epidemic curve
red curve, number of active infections over time, flatten the curve
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basic reproductive number (R0)
average number of susceptible individuals that a single infected individual infects
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disease will decline
R0
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disease will remain in population, but no outbreak or epidemic
R0=1
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disease will increase, and outbreaks are possible
R0>1
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what does basic reproductive number depend on?
disease, region/environment
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herd immunity
when a large portion of the population becomes immune to a disease, making the spread of disease unlikely
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what are 2 ways herd immunity can increase?

1. through immunity as a result of recovering from infection
2. through vaccination
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the _________ is a critical value in understanding what percentage of the population is needed to be vaccinated to obtain herd immunity
basic reproductive number
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critical information threshold
minimum number of individuals that need to be vaccinated to reach herd immunity
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small R0=
less of the population needs to be vaccinated
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larger R0=
much more of the population needs to be vaccinated
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community
set of interacting populations of species in the same living area
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direct community interactions
predation, competition, mutualism
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community structure
the identities of species an environment contains and how abundant each species is in that environment
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community composition
another name for community structure
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relative biomass
amount of biomass each individual contributes
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species diversity

1. quantifiable measure of community structure
2. the number of species a community contains
3. the number of individuals of each species in that community
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species richness
the number of species in a community
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species abundance
the number of individuals per species
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relative species abundance
proportion (or percentage) that each species contributes to the total number of individuals of all species in a community
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dominant species
species that contain the majority of individuals (or biomass) making up the community
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rare species
contains few individuals
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species evenness
an important characteristic of a community that refers to how equal the number of individuals are distributed across a species
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David Tilman
classic cedar creek experiment
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alpha diversity
species richness and evenness at a given location
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examples of alpha diversity
simpson’s index, shannon’s index
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simpson’s index
considers only species richness
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shannon’s index
both species richness and evenness
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beta diversity
the change in species identities and abundance across locations
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examples of beta diversity
Jaccar’s index, Bray-Curtis index
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Jaccard’s index
only species identity
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Bray-Curtis Index
species identity and abundance
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3 trophic levels
carnivore, herbivore, primary predator
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indirect mutualism
when a higher trophic level benefits abundance of another trophic level through indirect interactions
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trophic cascades
when the addition or removal of a top predator causes changes in population sizes throughout the food web
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keystone species
a specie that has a disproportionate effect on the community relative to its abundance
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Top-down control
the world is green because carnivores control herbivores, which allows for plant species biomass to remain high
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bottom-up control
the amount of plant species biomass determines how many trophic levels the environment can support
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Fredrick E Clements
viewed communities as superorganisms
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Henry A Gleason
viewed species as independent, and communities are not superorganisms
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ecotone
distinct transitional zones between community types
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examples of ecotones
aquatic-terrestrial, grassland-forest, north versus west slopes
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robert whittaker
one of the first to collect enough data to test whether clement’s or gleason’s view of the world was correct
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regional species pool
which species COULD make up a community
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community assembly
a more modern day view of what determines species identity and their abundance in a given community
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dispersal
often times a random process
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environmental filters
are the abiotic conditions suitable?
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species assembly
determined by random chance, environmental filters and species interactions
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species sorting
once species establish populations in a community, all of the interactions determine who stays and whose population grows
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community dynamics
change in species composition over time; usually response to a minor or major disturbance
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disturbance
an event that removes or changes the abundance of a species in a community
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catastrophic disturbance
destroys all members of the community and exposes new substrate
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non-catastrophic to minor disturbance
removes some species, or changes the abundance of some species; forest fires, invasive species, harsh winter, drought, nutrient pollution
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succession
directional change in community composition over time
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primary succession
occurs after catastrophic disturbance on newly exposed geological substrates that haven’t been modified by organisms; ex: new lava, newly exposed islands, melting glaciers, newly formed sand dunes
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secondary succession
occurs after non-catastrophic disturbance kills some members of a community but leaves the substrate intact
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chronosequence
selecting and studying sites differing in known ages; ex: sand dunes
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Henry Cowles
used a chronosequence of different sand dunes of known age to study succession; determined sand dune ages of Lake Michigan based on historical photos; used primary succession
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Peter Vitousek
chronosequence of Hawaiian islands to study primary succession of biological communites
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william cooper
established long term monitoring plots in areas that were recently exposed because of melting glaciers
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pioneer species
early successional species; good dispersers, fast growers, can tolerate harsh conditions, but are poor competitors and are short lived
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late successional species
poor dispersers, slower growers, require developed substrate, are good competitors, and tend to be long lived
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autogenic
when environmental changes are caused by species in the community; ex: glacier bay national park
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intermediate disturbance hypothesis
species diversity is highest under moderate disturbance
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what does community response to disturbance depend on?
disturbance regime (type, timing, severity, spatial extent, frequency), how the species making up the community and how they respond (resistance, return/recovery time, resilience)
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resistance
indicates the degree to which a community is altered by disturbance
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recovery time
time in which a disturbance-altered community returns to its original structure
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resiliency
indicates the degree to which communities return to their original community structure following the disturbance
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shifting mosaic
landscapes are dynamic, shifting community types over time because of small disturbances
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climax community
end point succession; community is at equilibrium; no change in species composition with time; assumes disturbances are no longer occurring
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landscape ecology
focuses on processes that lead to change in species composition across larger scales
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patches
distinct communities or ecosystems
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matrix
surrounding area that differs from the patch (can be a barrier to dispersal)
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boundary
area of transition between patch and matrix
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functional connectivity
degree to which landscape allows movement
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tyson research center glade experiment
lots of large scale manipulative experiments looking at the effect of patch size on species diversity
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glades
unique plant communities in forests similar to prairies; historically maintained by fire
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two prominent models in landscape ecology

1. theory of island biogeography
2. metapopulation theory
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theory of island biogeography
EO WIlson, Robert MacArthur; predicts species diversity based on patch size and isolation from mainland (species pool); predicts the number of species occupying a patch is determined by a balance of immigration and extinction
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immigration
number of new species colonizing; rate of immigration declines with number of species already established on patch; less niches available, more competition
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local extinction
loss of species from a patch (island); more isolated islands will have higher rates of local extinction; a species population on closer islands have higher chance of being rescued from a population established on the mainland
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metapopulation
a group of spatially distinct subpopulations, but are not reproductively isolated (gene flow can occur among subpopulations)