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Chapter 54CommunityEcology
Overview: A Sense of Community
A biological community is an assemblage ofpopulations of various species living close enoughfor potential interaction
Concept 54.1Community interactions areclassified by whether they help,harm, or have no effect on thespecies involved
Ecologists call relationships between species in acommunity interspecific interactionsExamples are competition, predation, herbivory, andsymbiosis (parasitism, mutualism, and commensalism)Interspecific interactions can affect the survival andreproduction of each species, and the effects can besummarized as positive (+), negative ( ), or no effect (0)
CompetitionInterspecific competition ( / interaction) occurswhen species compete for a resource in shortsupply
Competition: Competitive Exclusion
Strong competition can lead to competitiveexclusion, local elimination of a competing speciesThe competitive exclusion principle states that twospecies competing for the same limiting resourcescannot coexist in the same place
Competition: Ecological Niches
ecological nicheAn ecological niche can also be thought of as an
Ecologically similar species can coexist in acommunity if there are one or more significantdifferences in their nichesResource partitioning is differentiation of ecologicalniches, enabling similar species to coexist in acommunity
A. ricordii
A. insolitus usually percheson shady branches.
A. distichus perches on fenceposts and other sunny surfaces.
A. alinigerA. distichus
A. insolitus
A. christophei
A. cybotesA. etheridgei
niche may differ from its realized niche
Ocean
ChthamalusBalanus
EXPERIMENT
RESULTS
High tide
Low tide
Chthamalusrealized niche
Balanusrealized niche
High tide
Chthamalusfundamental niche
Low tideOcean
Competition: CharacterDisplacement
Character displacement isa tendency forcharacteristics to be moredivergent in sympatricpopulations of two speciesthan in allopatricpopulations of the sametwo speciesAn example is variation inbeak size betweenpopulations of two speciesof Galápagos finches
Los Hermanos
G. fuliginosaG. fortis
Beakdepth
Daphne
G. fuliginosa,allopatric
G. fortis,allopatric
Sympatricpopulations
Santa María, San Cristóbal
Beak depth (mm)
6040200
6040200
6040200
8 10 12 14 16
PredationPredation (+/ interaction) refers to interactionwhere one species, the predator, kills and eats theother, the preySome feeding adaptations of predators are claws,teeth, fangs, stingers, and poisonPrey display various defensive adaptationsBehavioral defenses include hiding, fleeing, formingherds or schools, self-defense, and alarm callsAnimals also have morphological and physiologicaldefense adaptations
PredationCryptic coloration, orcamouflage, makes preydifficult to spotAnimals with effectivechemical defense oftenexhibit bright warningcoloration, calledaposematic coloration
Predators are particularlycautious in dealing withprey that display suchcoloration
Canyon tree frog(a)Cryptic
coloration
Poison dart frog(b)Aposematic
coloration
PredationIn some cases, a prey species may gain significantprotection by mimicking the appearance ofanother speciesIn Batesian mimicry, a palatable or harmless speciesmimics an unpalatable or harmful modelIn Müllerian mimicry, two or more unpalatablespecies resemble each other
(c) Batesian mimicry: A harmless species mimics a harmful one.Hawkmothlarva
Green parrot snakeYellow jacketCuckoo bee
Müllerian mimicry: Two unpalatable speciesmimic each other.
(d)
HerbivoryHerbivory (+/ interaction) refers to an interaction inwhich an herbivore eats parts of a plant or algaIt has led to evolution of plant mechanical andchemical defenses and adaptations by herbivores
SymbiosisSymbiosis is a relationship where two or morespecies live in direct and intimate contact with oneanother
Symbiosis: ParasitismIn parasitism (+/ interaction), one organism, theparasite, derives nourishment from anotherorganism, its host, which is harmed in the processParasites that live within the body of their host arecalled endoparasites; parasites that live on theexternal surface of a host are ectoparasitesMany parasites have a complex life cycle involvinga number of hostsSome parasites change the behavior of the host toincrease their own fitness
Symbiosis:Mutualism
Mutualistic symbiosis, ormutualism (+/+interaction), is aninterspecific interactionthat benefits bothspeciesA mutualism can be
Obligate, where onespecies cannot survivewithout the otherFacultative, where bothspecies can survivealone
(a) Acacia tree and ants (genus Pseudomyrmex)
(b) Area cleared by ants at the base of an acacia tree
Symbiosis: CommensalismIn commensalism (+/0 interaction), one speciesbenefits and the other is apparently unaffectedCommensal interactions are hard to document innature because any close association likely affectsboth species
Concept 54.2Dominant and keystone speciesexert strong controls on communitystructure
In general, a few species in a community exertstructure
Two fundamental features of communitystructure are species diversity and feedingrelationships
Species DiversitySpecies diversity of a community is the variety oforganisms that make up the communityIt has two components: species richness andrelative abundanceSpecies richness is the total number of differentspecies in the communityRelative abundance is the proportion each speciesrepresents of the total individuals in the community
Community 1A: 25% B: 25% C: 25% D: 25%
Community 2A: 80% B: 5% C: 5% D: 10%
A B C D
Species DiversityTwo communities can have the same speciesrichness but a different relative abundanceDiversity can be compared using a diversity index
Shannon diversity index (H):H = [(pA ln pA) + (pB ln pB) + (pC ln pC) +
Determining the number and abundance ofspecies in a community is difficult, especially forsmall organismsMolecular tools can be used to help determinemicrobial diversity
Soil pH
3.6
RESULTS
3.4
3.2
3.0
2.8
2.6
2.4
2.23 4 5 6 7 8 9
Trophic StructureTrophic structure is thefeeding relationshipsbetween organisms in acommunityIt is a key factor incommunity dynamicsFood chains link trophiclevels from producers totop carnivores
Carnivore
Carnivore
Carnivore
Herbivore
Plant
A terrestrial food chain
Quaternaryconsumers
Tertiaryconsumers
Secondaryconsumers
Primaryconsumers
Primaryproducers
A marine food chainPhytoplankton
Zooplankton
Carnivore
Carnivore
Carnivore
Trophic Structure: Food WebsA food web is a branching food chain with complextrophic interactions
Humans
Smallertoothedwhales
Baleenwhales
Spermwhales
Elephantseals
Leopardseals
Crab-eaterseals
Birds Fishes Squids
Carnivorousplankton
CopepodsEuphausids(krill)
Phyto-plankton
Trophic Structure: Food WebsSpecies may play a role at more than one trophiclevelFood webs can be simplified by isolating a portionof a community that interacts very little with the restof the community
Sea nettle
Fish larvae
Juvenile striped bass
Fish eggs Zooplankton
Trophic Structure: Limits on FoodChain Length
Each food chain in a food web is usually only a fewlinks longTwo hypotheses attempt to explain food chainlength: the energetic hypothesis and the dynamicstability hypothesisThe energetic hypothesissuggests that length is limitedby inefficient energy transferThe dynamic stabilityhypothesis proposes that longfood chains are less stablethan short onesMost data support the energetic hypothesis
Productivity
012345
High (control):natural rate of
litter fall
Medium: 1/10natural rate
Low: 1/100natural rate
Species with a Large ImpactCertain species have a very large impact oncommunity structureSuch species are highly abundant or play a pivotalrole in community dynamics
Species with a Large Impact:Dominant Species
Dominant species are those that are most abundant orhave the highest biomassBiomass is the total mass of all individuals in a populationDominant species exert powerful control over theoccurrence and distribution of other speciesOne hypothesis suggests that dominant species are mostcompetitive in exploiting resourcesAnother hypothesis is that they are most successful atavoiding predatorsInvasive species, typically introduced to a newenvironment by humans, often lack predators or disease
Species with a Large Impact:Keystone Species
Keystone species exert strong control on acommunity by their ecological roles, or nichesIn contrast to dominant species, they are notnecessarily abundant in a communityField studies of sea stars exhibit their role as akeystone species in intertidal communities
EXPERIMENT
With Pisaster (control)
Without Pisaster (experimental)
Year
20
15
10
5
01963
RESULTS
Species with aLarge Impact:KeystoneSpecies
Observation of seaotter populationsand their predationshows how ottersaffect oceancommunities
(a) Sea otter abundance
100
80
60
40
200
400300200100
0(b) Sea urchin biomass
1086420
1972 1985 1997Year
(c) Total kelp densityFood chain
1989 1993
Species with a Large Impact:Foundation Species (Ecosystem
physical changes in the environment that affectcommunity structureFor example, beaver dams can transformlandscapes on a very large scale
Species with a Large Impact:Foundation Species (Ecosystem
Some foundation species act as facilitators thathave positive effects on survival and reproductionof some other species in the community
With Juncus Without Juncus0
2
4
6
8
Salt marsh with Juncus(foreground)
(a) (b)
Bottom-Up and Top-Down Controls
The bottom-up model of community organizationproposes a unidirectional influence from lower tohigher trophic levelsIn this case, presence or absence of mineralnutrients determines community structure, includingabundance of primary producersThe top-down model, also called the trophiccascade model, proposes that control comes fromthe trophic level aboveIn this case, predators control herbivores, which inturn control primary producers
Bottom-Up and Top-Down ControlsLong-term experimental studies have shown thatcommunities vary in their relative degree of bottom-up to top-down control
Control plotsWarmed plots
E. antarcticus S. lindsayae0
100
200
300
RESULTS
Bottom-Up and Top-Down ControlsPollution can affect community dynamicsBiomanipulation can help restore pollutedcommunities
Polluted State Restored State
Rare
Rare Abundant
AbundantFish
Zooplankton
Algae Abundant Rare
Concept 54.3Disturbance influences speciesdiversity and composition
Decades ago, most ecologists favored the view thatcommunities are in a state of equilibriumThis view was supported by F. E. Clements who suggestedthat species in a climax community function as asuperorganismOther ecologists, including A. G. Tansley and H. A.Gleason, challenged whether communities were atequilibriumRecent evidence of change has led to a nonequilibriummodel, which describes communities as constantlychanging after being buffeted by disturbances
Characterizing DisturbanceA disturbance is an event that changes acommunity, removes organisms from it, and altersresource availabilityFire is a significant disturbance in most terrestrialecosystemsIt is often a necessity in some communities
The intermediate disturbance hypothesis suggeststhat moderate levels of disturbance can fostergreater diversity than either high or low levels ofdisturbanceHigh levels of disturbance exclude many slow-growing speciesLow levels of disturbance allow dominant species toexclude less competitive species
Log intensity of disturbance
30
20
15
101.1 1.2 1.3 1.4 1.5 1.6 1.7 1.8 1.9 2.0
35
25
1.00.9
Characterizing DisturbanceThe large-scale fire in Yellowstone National Park in1988 demonstrated that communities can oftenrespond very rapidly to a massive disturbance
(a) Soon after fire (b) One year after fire
Ecological SuccessionEcological succession is the sequence ofcommunity and ecosystem changes after adisturbancePrimary succession occurs where no soil exists whensuccession beginsSecondary succession begins in an area where soilremains after a disturbanceEarly-arriving species and later-arriving species maybe linked in one of three processes:
Early arrivals may facilitate appearance of laterspecies by making the environment favorableThey may inhibit establishment of later speciesThey may tolerate later species but have no impacton their establishment
Retreating glaciers provide a valuable field-research opportunity for observing successionSuccession on the moraines in Glacier Bay, Alaska,follows a predictable pattern of change invegetation and soil characteristics
Pioneer stage, withfireweed dominant
1
19411907
1860
1760
Alaska
GlacierBay
Kilometers5 10 150
Dryas stage2
Alder stage3Spruce stage4
Succession is the result of changes induced by thevegetation itselfOn the glacial moraines, vegetation lowers the soilpH and increases soil nitrogen content
Successional stagePioneer Dryas Alder Spruce
0
10
20
30
40
50
60
Human DisturbanceHumans have the greatest impact on biologicalcommunities worldwideHuman disturbance to communities usually reducesspecies diversityHumans also prevent some naturally occurringdisturbances, which can be important tocommunity structure
Concept 54.4Biogeographic factors affectcommunity biodiversity
Latitude and area are two key factors that affect
Latitudinal GradientsSpecies richness generally declines along anequatorial-polar gradient and is especially great inthe tropicsTwo key factors in equatorial-polar gradients ofspecies richness are probably evolutionary historyand climateThe greater age of tropical environments mayaccount for the greater species richness
Latitudinal GradientsClimate is likely the primary causeof the latitudinal gradient inbiodiversityTwo main climatic factorscorrelated with biodiversity aresolar energy and water availabilityThey can be considered together
of evapotranspirationEvapotranspiration is evaporationof water from soil plus transpirationof water from plants
(a) TreesActual evapotranspiration (mm/yr)
180
160
140
120
100
80
60
20
0
40
100 300 500 700 900 1,100
(b) Vertebrates
200
100
50
100 500 1,000 1,500 2,000
Potential evapotranspiration (mm/yr)
Area EffectsThe species-area curve quantifies the idea that, allother factors being equal, a larger geographic areahas more speciesA species-area curve of North American breedingbirds supports this idea
Area (hectares)
1,000
100
10
10.1 1 10 100 103 104 105 106 107 108 109 1010
Island Equilibrium ModelSpecies richness on islands depends on island size,distance from the mainland, immigration, andextinctionThe equilibrium model of island biogeographymaintains that species richness on an ecologicalisland levels off at a dynamic equilibrium point
Number of species on islandEquilibrium number
(a) Immigration and extinction rates
Number of species on island
(b) Effect of island size
Small island Large island
(c) Effect of distance from mainland
Number of species on islandFar island Near island
Island Equilibrium ModelStudies of species richness on the Galápagos Islandssupport the prediction that species richnessincreases with island size
Area of island (hectares)(log scale)
10 100 103 104 105 106
10
2550
100200
400
5
Concept 54.5Community ecology is useful forunderstanding pathogen life cyclesand controlling human disease
Ecological communities are universally affectedby pathogens, which include disease-causingmicroorganisms, viruses, viroids, and prionsPathogens can alter community structure quicklyand extensively
Pathogen and Community Structure
Pathogens can have dramatic effects oncommunitiesFor example, coral reef communities are beingdecimated by white-band diseaseHuman activities aretransporting pathogensaround the world atunprecedented ratesCommunity ecology isneeded to help studyand combat them
Community Ecology and ZoonoticDiseases
Zoonotic pathogens have been transferred fromother animals to humansThe transfer of pathogens can be direct or throughan intermediate species called a vector
zoonoticAvian flu is a highly contagious virusof birdsEcologists are studying the potentialspread of the virus from Asia toNorth America through migratingbirds