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    Copyright 2008 Pearson Education, Inc., publishing as Pearson Benjamin Cummings

    PowerPointLecture Presentations for

    BiologyEighth Edition

    Neil Campbell and Jane Reece

    Lectures by Chris Romero, updated by Erin Barley with contributions from Joan Sharp

    Chapter 54

    Community Ecology

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    Overview: A Sense of Community

    A biological communityis an assemblage of

    populations of various species living close enough forpotential interaction. All life / all populations in anarea.

    Ecologists call relationships between speciesin acommunity interspecific interactions.

    Interspecific interactions can affect the survival andreproduction of each species. Effects can be positive

    (+), negative (), or no effect (0). Examples: competition, predation, herbivory, and

    symbiosis (parasitism, mutualism, commensalism).

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    Competition

    Interspecific competition(/ interaction)occurs when different species compete for aresource in short supply.

    Strong competition can lead to competitive

    exclusion, local elimination of a competingspecies.

    The competitive exclusion principlestates

    that two species competing for the samelimiting resources cannot coexist in the sameplace = 1 species per niche.

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    Ecological Niches The total of a species use of biotic and abiotic

    resourcesis called the speciesecological niche.

    An ecological niche can also be thought of as anorganisms ecological role.

    Ecologically similar species can coexist in acommunity if there are one or more significantdifferences in their niches.

    Resource partitioningis differentiation of ecologicalniches; enables similar species to coexist in acommunity.

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    Resourcepartitioningisdifferentiation

    ofecologicalniches,enablingsimilarspeciesto coexist

    in acommunity

    A. ricordii

    B. lizard speciesusually percheson shady branches.

    A. Lizard speciesperches onfences and other sunny surfaces.

    A. aliniger

    A. distichus

    A. insolitus

    A. christophei

    A. cybotes

    A. etheridgei

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    As a result of interspecific competition, aspecies fundamental niche may differ from itsrealized niche --> the niche it occupys afterresource partitioning.

    Interspecific => Competition Between Species:Can Lead to Resource Partitioning

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    How aspecies

    niche can beinfluenced

    byinterspecificcompetition?

    Ocean

    Chthamalus

    Balanus

    Later - Realized Niche

    Ist - Fundamental Niche

    High tide

    Low tide

    Chthamalus

    realized niche

    Balanus

    realized niche

    High tide

    Chthamalus

    fundamental niche

    Low tideOcean

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    Character Displacement

    Character displacementis a tendency forcharacteristics / particular traits to be moredivergent in sympatric populations of twospecies than in allopatric populations of the

    same two species.

    An example is variation in beak size betweenpopulations of two species of Galpagos

    finches.

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    Characterdisplacement:

    IndirectEvidenceof PastCompetition Los Hermanos

    G. fuliginosa G. fortis

    Beakdepth

    Daphne

    G. fuliginosa,allopatric

    G. fortis,allopatric

    Sympatricpopulations

    Santa Mara, San Cristbal

    Beak depth (mm)

    Percentages

    ofindividualsin

    eachsizeclass

    60

    40

    20

    0

    60

    40

    20

    0

    6040

    20

    08 10 12 14 16

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    Predation

    Predation(+/ interaction) refers to interactionwhere one species, the predator, kills and eatsthe other, the prey.

    Some feeding adaptations of predators areclaws, teeth, fangs, stingers, and poison.

    Prey display various defensive adaptations:

    such as behavior and coloration.

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    Behavioraldefenses include hiding, fleeing, formingherds or schools, self-defense, and alarm calls.

    Animals also have morphologicalandphysiologicaldefense adaptations:

    Cryptic coloration= camouflage, makes prey difficultto spot.

    Aposematic coloration: Animals with effectivechemical defense /poison/ often exhibit brightwarning coloration. Predators are particularly cautiousin dealing with prey that display such coloration.

    Prey: Defensive Adaptations

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    Canyon tree frog

    (a) Crypticcoloration

    (b) AposematiccolorationPoison dart frog

    (c) Batesian mimicry: A harmless species mimics a harmful one.Hawkmothlarva

    Green parrot snakeYellow jacketCuckoo bee

    Mllerian mimicry: Two yuckunpalatable species mimic each other.

    (d)

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    In some cases, a prey species may gainsignificant protection by mimicking theappearance of another species:

    In Batesian mimicry, a harmless speciesmimics an unpalatable or harmful model Oneis apretender.

    In Mllerian mimicry, two or more unpalatablespecies resemble each other BOTHareyuck.

    Mimicry = Look-alikes Defense

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    Herbivory: Herbivores = Plant Predators

    Herbivory (+/ interaction) refers to aninteraction in which an herbivore eats parts of aplant or alga.

    It has led to evolution of plant defensesagainst herbivores: secondary compounds=are chemical defenses; and mechanicaldefenses which are often osmoregulated.

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    Symbiosis: + + + 0 + -

    Symbiosisis a dependency relationshipwheretwo or more species live in direct and intimatecontact with one another. The relationship isgenerally based one or some combination of

    the following benefits:

    Nutrition (food, water)

    Protection

    Reproduction

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    Parasitism + -

    In parasitism (+/ interaction), one organism, theparasite, derives nourishment from another organism,its host, which is harmed in the process.

    Endoparasites = parasites that live within the body of

    their host. Ectoparasites = parasites that live on the external

    surface of a host.

    Many parasites have a complex life cycle involving anumber of hosts.

    Some parasites change the behavior of the host toincrease their own fitness (reproduce more offspring).

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    Mutualism + +

    Mutualistic symbiosis, or mutualism(+/+interaction), is an interspecific interaction thatbenefits both species.

    A mutualism can be: Obligate = MUSTwhere one species cannot

    survive without the other.

    Facultative = OPTIONAL where both speciescan survive alone.

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    Commensalism + 0

    In commensalism (+/0 interaction), onespecies benefits and the other is apparentlyunaffected.

    Commensal interactions are hard to documentin nature because any close association likelyaffects both species.

    A ibl l f li b t ttl t (bi d ) d t

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    A possible example of commensalism between cattle egrets (birds) and waterbuffalo: The Birds eat insects disturbed by the Buffalo as they move.

    D i t d k t i t t

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    Dominant and keystone species exert strongcontrols on community structure

    A few species in a community often exertstrong control on that communitys structure.

    Two fundamental features of community

    structure = species diversity and feedingrelationships.

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    Species Diversity

    Species diversityof a community is the

    variety of organisms that make up thecommunity.

    It has two components: species richness and

    relative abundance.

    Species richness is the total number ofdifferent species in the community.

    Relative abundance is the proportion eachspecies represents of the total individuals in thecommunity.

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    Trophic Structure = a key factor in communitydynamics

    Trophic structureis the feeding relationshipsbetween organisms in a community.

    Food chains link trophic levels from producers to topcarnivores.

    A food web is a branching food chain with complextrophic interactions.

    Species may play a role at more than one trophiclevel.

    Food chains in a food web are usually only a few linkslong. WHY?

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    TerrestrialandMarine

    FoodChains

    Carnivore

    Carnivore

    Carnivore

    Herbivore

    Plant

    A terrestrial food chain

    Quaternaryconsumers

    Tertiaryconsumers

    Secondaryconsumers

    Primaryconsumers

    Primaryproducers

    A marine food chain

    Phytoplankton

    Zooplankton

    Carnivore

    Carnivore

    Carnivore

    An Antarctic

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    An AntarcticMarineFood Web

    Humans

    Smaller

    toothedwhales

    Baleenwhales Spermwhales

    Elephantseals

    Leopardseals

    Crab-eaterseals

    Birds Fishes Squids

    Carnivorous

    plankton

    CopepodsEuphausids(krill)

    Phyto-plankton

    Li i F d Ch i L h

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    Limits on Food Chain Length Food chains in food webs are usually only a few links

    long.

    Two hypotheses attempt to explain food chain length:the energetic hypothesisand the dynamic stability

    hypothesis. The energetic hypothesissuggests that length is

    limited by inefficient energy transfer.

    The dynamic stability hypothesis proposes that longfood chains are less stable than short ones.

    Most data support the energetic hypothesis.

    S i i h L I

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    Species with a Large Impact

    Certain species have a very large impact oncommunity structure. Such species are highlyabundantOR play a pivotal rolein communitydynamics.

    Dominant species= those that are mostabundant or have the highest biomass.

    Biomassis the total mass of all individuals in apopulation. Dominant species exert powerfulcontrol over the occurrence and distribution ofother species.

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    Invasive species, typically introduced to a newenvironment by humans, often lack predatorsor disease pathogens. Invasive species disruptecosystem dynamics. They frequently out-

    compete / displace native populations.

    K t S i

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    Keystone Species Keystone speciesexert strong control on a

    community by their ecological roles, or niches.

    In contrast to dominant species, they are notnecessarily abundant in a community.

    Field studies of sea stars exhibit their role as akeystone species in intertidal communities.

    Sea otter populations and their predationshows how otters affect ocean communities.Sea otters are keystone predators in the North

    Pacific.

    Seastar are

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    Seastar arekeystonepredators.They are key

    in preservingspeciesdiversity intheir

    ecosystem.

    With Pisaster(control)

    Without Pisaster(experimental)Numberofspecies

    present

    Year

    20

    15

    10

    5

    01963 64 65 66 67 68 69 70 71 72 73

    RESULTS

    EXPERIMENT

    Sea otters

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    Sea ottersarekeystone

    predatorsin theNorthPacific

    (a) Sea otter abundance

    O

    tternumber

    (%

    max.count)

    100

    80

    60

    40

    20

    0

    400

    300

    200

    100

    0(b) Sea urchin biomass

    Grams

    per

    0.2

    5m

    2

    10

    8642

    01972

    Numberp

    er

    0.2

    5m

    2

    1985 1997Year

    (c) Total kelp densityFood chain

    1989 1993

    F d ti S i (E t E i )

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    Foundation Species (Ecosystem Engineers)

    Foundation species (ecosystem engineers)cause physical changes in the environmentthat affect community structure.

    For example, beaver dams can transformlandscapes on a very large scale.

    Some foundation speciesact asfacilitators

    that have positive effects on survival andreproduction of some other speciesin thecommunity.

    Beavers are a Foundation Species = ecosystemengineers

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    Beavers are a Foundation Species = ecosystem engineers

    B tt U d T D C t l

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    Bottom-Up and Top-Down Controls

    The bottom-up model of community

    organization proposes a unidirectionalinfluence from lower to higher trophic levels.

    In this case, presence or absence of mineral

    nutrients determines community structure,including abundance of primary producers.

    The top-down model, also called the trophic

    cascade model,proposes that control comesfrom the trophic level above.

    In this case, predators control herbivores,which in turn control primary producers.

    Disturbance influences species diversity and

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    Disturbance influences species diversity andcomposition

    Pollution can affect community dynamics.

    Biomanipulation can help restore pollutedcommunities. Bio remediationis an effectivestrategy to restorepolluted and damaged

    areas.

    Decades ago, most ecologists favored the viewthat communities are in a state of equilibrium.

    Recent evidence of change has led to anonequilibrium model, which describescommunities as constantly changing after

    being buffeted by disturbances.

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    The large-scale fire in Yellowstone National Park in 1988

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    The large scale fire in Yellowstone National Park in 1988demonstrated that communities can often respond very rapidlyto a massive disturbance.

    (a) Soon after fire (b) One year after fire

    Ecological Succession

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    Ecological Succession

    Ecological successionis the

    sequence ofcommunity and ecosystem changesafter adisturbance, over time.

    Primary successionoccurs where no soilexists when succession begins. Pioneerorganisms, such as lichen, are the foundationof the community and soil building.

    Secondary successionbegins in an areawhere soil remainsafter a disturbance /disastersuch as fire or field abandonment.

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    Early-arriving species and later-arriving species

    may be linked in one of three processes:

    Early arrivals may facilitate appearance of laterspecies by making the environment favorable

    They may inhibit establishment of later species

    They may tolerate later species but have no

    impact on their establishment Glacier retreating -- predictable pattern of

    ecologial succession

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    Pioneer stage = soil builders / fireweed dominant1

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    Dryasstage grasses and shrubs2

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    Alder stage: trees and shrub3

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    Spruce stage = Climax Community STABLE4

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    Changes in soil nitrogen content during succession at Glacier

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    g g gBay

    Successional stage

    Pioneer Dryas Alder Spruce

    Soilnitrogen(g/m2)

    0

    10

    20

    30

    40

    50

    60

    Human Disturbance

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    Human Disturbance

    Humans have the greatest impact on biologicalcommunities worldwide. Human disturbance tocommunities usually reduces species diversity.

    Humans also prevent some naturally occurringdisturbances, which can be important tocommunity structure.

    Disturbance of the ocean floor by trawling

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    y g

    Biogeographic factors affect community

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    Biogeographic factors affect communitybiodiversity

    Latitudeandareaare two key factors that

    affect a communitys species diversity.

    Species richness generally declines along anequatorial-polar gradient and is especially great

    in the tropics. Two key factors in equatorial-polar gradientsof

    species richness are probably evolutionary

    historyandclimate. The greater age of tropical environments may

    account for the greater species richness.

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    Climate is likely the primary cause of the

    latitudinal gradient in biodiversity.

    Two main climatic factors correlated withbiodiversity are solar energy and water

    availability. They can be considered togetherby measuring a communitys rate of

    evapotranspiration.

    Evapotranspiration is evaporation of waterfrom soil plus transpiration of water from plants.

    Area Effects

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    Area Effects

    The species-area curve quantifies the ideathat, all other factors being equal, a largergeographic area has more species.

    A species-area curve of North Americanbreeding birds supports this idea.

    Island Equilibrium Model

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    Island Equilibrium Model

    Species richness on islands depends onisland size, distance from the mainland,immigration, and extinction.

    The equilibrium model of island biogeography

    maintains that species richness on anecological island levels off at a dynamicequilibrium point.

    Studies of species richness on the GalpagosIslands support the prediction that speciesrichness increases with island size.

    The equilibrium model of island biogeography

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    The equilibrium model of island biogeography

    Number of species on island

    Equilibrium number

    (a) Immigration and extinction rates

    Rateofimmig

    rationorextinction

    Rateofimmig

    rationorextinction

    Number of species on island

    (b) Effect of island size

    Small island Large island

    (c) Effect of distancefrom mainland

    Number of species on island

    Rateofimmig

    rationorextinction

    Far island Near island

    Community ecology is useful for understanding

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    Community ecology is useful for understandingpathogen life cycles and controlling human disease

    Ecological communities are universally affectedby pathogens, which include disease-causingmicroorganisms, viruses, viroids, and prions.

    Pathogens can alter community structurequickly and extensively.

    For example, coral reef communities are beingdecimated by white-band disease.

    White-band disease on coral is destroying the reef.

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    Community Ecology and Zoonotic Diseases

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    Co u ty co ogy a d oo ot c seases

    Human activities are transporting pathogens around

    the world at unprecedented rates. Community ecology is needed to help study and

    combat them.

    Zoonotic pathogens have been transferred from otheranimals to humans.

    The transfer of pathogenscan be direct or through anintermediate species called a vector.

    Many of todays emerging human diseases arezoonotic. Avian flu is a highly contagious virus of birds.

    Review

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    You should now be able to:

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    1. Distinguish between the following sets ofterms: competition, predation, herbivory,symbiosis; fundamental and realized niche;cryptic and aposematic coloration; Batesian

    mimicry and Mllerian mimicry; parasitism,mutualism, and commensalism;endoparasites and ectoparasites; speciesrichness and relative abundance; food chainand food web; primary and secondarysuccession.

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    2. Define an ecological niche and explain thecompetitive exclusion principle in terms of theniche concept.

    3. Explain how dominant and keystone speciesexert strong control on community structure.

    4. Distinguish between bottom-up and top-down

    community organization.

    5. Describe and explain the intermediatedisturbance hypothesis.

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    6. Explain why species richness declines alongan equatorial-polar gradient.

    7. Define zoonotic pathogens and explain, with

    an example, how they may be controlled.