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Populations Outline: Properties of populations Population growth Intraspecific population Metapopulation Readings: Ch. 9, 10, 11, 12
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Definition Population is a group of individuals of the same species that inhabit a given area
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Unitary organisms
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Modular organisms
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genet ramet
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Distribution of a population
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Red maple
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Distribution of a population Moss (Tetraphis pellucida)
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Abundance versus Population density
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Patterns of dispersion
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Effect of scale on pattern of dispersion
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Populations have age structure
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Determining age
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wild turkeyquail grey squirelbat Determining age
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Dispersal Movement of individuals in space Moving out of subpopulation = emigration Moving into a subpopulation = immigration Moving and returning= migration
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Yellow-poplar
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Ring-necked duck Gray whale
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Gypsy-moth
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POPULATION GROWTH
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Darwin’s 1 st observation: All species have such great potential fertility that their population size would increase exponentially if all individuals that are born reproduce successfully.
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Example of exponential growth: the ring-necked pheasant, Phasianus colchicus Native to Eurasia 1937: Eight birds introduced to Protection Island (Washington state) 1942: Population had increased to 1,325 birds (a 166-fold increase!)
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N/ t = (b - d) N t
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Population Growth Models Assume no immigration or emigration Let N = population size Let N/ t = change in population size/unit time = total # births - total # deaths Let mean birth rate per individual = b = # births / individual / unit time Let mean death rate per individual = d = probability of death for an individual / unit time N/ t = bN - dN Let r = b-d
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Population Growth Models r = instantaneous rate of increase a.k.a. per capita rate of increase Calculus notation is commonly used; N/ t = dN/dt If r > 0, population will increase exponentially at rate, dN/dt, = rN For an exponentially growing population, the number of individuals at time t, N t = N 0 e (rt) where N o = initial population size and e = base of natural logarithms
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Exponential growth model: N t = N 0 e (rt)
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St. Paul reindeer
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Life tables cohort - all individuals born within a period cohort life table – survivorship of a cohort over time
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l x = represents the probability at birth of surviving to any given age Life tables
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d x = represents the age-specific mortality Life tables
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q x = represents the age-specific mortality rate Life tables
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Mortality curves
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sedum Mortality curves
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Survivorship curves - plot of l x vs. time
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Red deer
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Theoretical survivorship curves
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What happened to population in 1940s?
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Human population growth
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Darwin’s 2 nd observation: Populations tend to remain stable in size, except for seasonal fluctuations Darwin’s 3 rd observation: Environmental resources are limited
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In real world, populations don’t increase exponentially for very long --> run out of resources An N increases, b decreases and/or d increases
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Population limiting factors Density-dependent: effect intensifies as N increases. E.g.: 1.Intraspecific competition – Between members of same species 2.Toxic waste accumulation – E.g. yeast cells: produce ethanol as by- product of fermentation (see next slide) 3.Disease – Spreads more easily in crowded environments
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Effect of crowding on birth rate
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Effect of crowding on survivorship
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Intraspecific population regulation
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Carrying capacity, K = maximum number of individuals that a particular environment can support Take into account by the Logistic Growth Equation, dN/dt = rN (1-N/K)
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Logistic model
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Exponential vs. logistic model Gray squirrel
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How good is the logistic model? Describes growth of simple organisms well, e.g. Paramecium in a lab Water fleas (Daphnia spp.): population initially overshoots K until individuals use up stored lipids --> crash down to K Song sparrows: populations crash frequently due to harsh winter conditions –N never have time to reach K –Population growth not well described by the logistic model
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Life History Strategies When N is usually << K, natural selection favors adaptations that increase r --> lots of offspring = r selection –E.g. species that colonize short-lived environments When N is usually close to K, better to produce fewer, “better quality” (i.e. more competitive) offspring = K selection E.g species that live in stable, crowded environments
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Density dependence
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with Allee effect
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American ginseng Density dependence with Allee effect
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Types of competition Competition: individuals use a common resource that is in short supply relative to the number seeking it Intraspecific vs. interspecific Scramble vs. contest Exploitation vs. interference
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Density effect on growth
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Horseweed Density effect on growth Self thinning
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Density effect on reproduction
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Territoriality
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Grasshopper sparrow Ammodramus savannarum
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Banding study in California: 24% of current territory holders had been floaters for 2- 5 yrs. before acquiring a territory. White-crowned sparrow, Zonotrichia leucophrys
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Uniform distribution of plants occurs due to the development of resource depletion zones around each individual
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Population limiting factors Density-independent: effect does not depend on N. –E.g. weather / climate –Thrips insects: Feed on Australian crops (pest) Population growth very rapid in early summer Drops in late summer due to heat, dryness --> N never has time to get close to K
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Density-independent factors
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DRY Turbid WET Clear Density-independent factors
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e.g. Dungeness crabs Density-dependent factors: competition; cannibalism Density-independent factors: water temperature
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Metapopulations a population of populations Chapter 12
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Metapopulation: A group of moderately isolated populations linked by dispersal
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Criteria for a metapopulation 1.Habitat occurs in discrete patches 2.Patches are not so isolated as to prevent dispersal 3.Individual populations have a chance of going extinct 4.The dynamics of populations in different patches are not synchronized – i.e., they do not fluctuate or cycle in synchrony
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Metapopulation dynamics: spatial scales 1.Local (within-patch) 2.Metapopulation (regional) Shifting mosaic of occupied and unoccupied patches
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Checkerspot butterfly
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Levin’s model of metapopulation dynamics E - subpopulation extinction rate = eP e – probability of a patch going extinct/unit time P – proportion of occupied patches C – colonization rate = mP (1-P) m – dispersal rate (1-P) – unoccupied habitats
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E = C equilibrium point, Where 0 = [mP(1-P)] - eP If C>E, P increases; If C<E, P decreases P equilibrium = 1-e/m
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Bush cricket
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Larger patches have larger populations (and therefore lower risk of extinction)
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Skipper butterfly
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Effect of habitat heterogeneity
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Mainland-island population structure: one large population (low extinction risk) provides colonists for many small populations (high risk) Rescue effect: island recolonized from “mainland” High quality / permanent population = source population Temporary patches = sink populations Checker-spot butterfly
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Skipper butterfly
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