Chapter 54 Community Ecology. Reminder: Earth Day April 22 nd, 2010.
-
Upload
eustace-lucas -
Category
Documents
-
view
218 -
download
3
Transcript of Chapter 54 Community Ecology. Reminder: Earth Day April 22 nd, 2010.
Chapter 54
Community Ecology
Reminder: Earth Day
April 22nd, 2010
Earth Day 2010 (40th anniversary of Earth day)
Iowa DNR 2009 self-assessment
The DNR also rated water quality at C-.
Numerically the water quality rated a D, but they gave themselves extra credit for effort!
Iowa’s water quality (DNR self-assessment)
A biological community– Is an assemblage of populations of various
species living close enough for potential interaction
The animals and plants surrounding this watering hole are all members of a savanna community in southern Africa
Community InteractionsA community’s interactions include competition, predation, herbivory, symbiosis, and disease
Populations are linked by interspecific interactions that affect the survival and reproduction of the species engaged in the interaction
Interspecific Interactions
Competition
Competition
Interspecific competition– Occurs when species compete for a particular
resource that is in short supply
Strong competition can lead to competitive exclusion– The local elimination of one of the two competing
species
The Competitive Exclusion Principle
The competitive exclusion principle– States that two species competing for the same
limiting resources cannot coexist in the same place
Ecological Niches
The ecological niche– Is the total of an organism’s use of the biotic
and abiotic resources in its environment
So if we take the niche concept into account– Then the competitive exclusion principle can be
reworded as:• Two species cannot coexist in a community if their
niches are identical
Ecologically similar species can coexist in a community. If there are one or more significant difference in their nichesFundamental niche (the niche potentially occupied) versus realized niche (the niche actually occupied)
When Connell removed Balanus from the lower strata, the Chthamalus population spread into that area.
The spread of Chthamalus when Balanus was removed indicates that competitive exclusion makes the realizedniche of Chthamalus much smaller than its fundamental niche.
RESULTS
CONCLUSION
Ocean
Ecologist Joseph Connell studied two barnacle speciesBalanus balanoides and Chthamalus stellatus that have a stratified distribution on rocks along the coast of Scotland.
EXPERIMENT
In nature, Balanus fails to survive high on the rocks because it isunable to resist desiccation (drying out) during low tides. Its realized niche is therefore similar to its fundamental niche. In contrast, Chthamalus is usually concentrated on the upper strata of rocks. To determine the fundamental of niche of Chthamalus, Connell removed Balanus from the lower strata.
Low tide
High tide
Chthamalusfundamental niche
Chthamalusrealized niche
Low tide
High tideChthamalus
Balanusrealized niche
Balanus
Ocean
As a result of competition– A species’ fundamental niche may be different
from its realized niche
A. insolitususually percheson shady branches.
A. distichus perches on fence posts and
other sunny surfaces.
A. distichus
A. ricordii
A. insolitus
A. christophei
A. cybotes
A. etheridgei
A. alinigar
Resource PartitioningResource partitioning is the differentiation of niches that enables similar species to coexist in a community
G. fortis
Beak depth (mm)
G. fuliginosa
Beak depth
Los Hermanos
Daphne
Santa María, San Cristóbal
Sympatric populations
G. fuliginosa, allopatric
G. fortis, allopatric
Per
cent
ages
of
indi
vidu
als
in e
ach
size
cla
ss40
20
0
40
20
0
40
20
0
8 10 12 14 16
Character DisplacementIn character displacement there is a tendency for characteristics to be more divergent in sympatric (geographically overlapping) populations of two species than in allopatric (geographically separate) populations of the same two speciesThe allopatric populations have similar beaks and use similar resources.
The sympatric populations would potentially compete for resources and their characteristics are more divergent
Predation
Predation
Predation refers to an interaction where one species, the predator, kills and eats the other, the prey
Adaptations– Feeding adaptations of predators include claws, teeth,
fangs, stingers, and poison
– animals also display a great variety of defensive adaptations to conteract predation
Predation (Hawk-snake)
Cryptic coloration, or camouflage makes prey difficult to spot
Aposematic coloration: warns predators to stay away from prey
Warning coloration in poisonous frogs (movie)
Mimicry
In some cases, one prey species– May gain significant protection by mimicking
the appearance of another
Batesian mimicry
Müllerian mimicry
In Batesian mimicry: A palatable or harmless species mimics an unpalatable or harmful model
(a) Hawkmoth larva
(b) Green parrot snake
In Müllerian mimicry– Two or more unpalatable species resemble each
other
(a) Cuckoo bee
(b) Yellow jacket
Fooling predators (movie)
HerbivoryParasitismDiseaseMutualismCommensalism
HerbivoryHerbivory– Has led to the evolution of plant mechanical
and chemical defenses and consequent adaptations by herbivores
ParasitismIn parasitism, one organism, the parasite– Derives its nourishment from another organism,
its host, which is harmed in the process
Parasitism can have a significant effect on survival, reproduction, density, and productivity of a populationEffects can be direct or indirect
Tomato Hornworm covered in cocoons of pupating parasitic wasp
Disease
Pathogens (disease-causing agents) have effects on populations and communities that are similar to that of parasites
Deer with Chronic Wasting Disease
Mutualism
Mutualistic symbiosis, or mutualism is an interspecific interaction that benefits both species
Mutualism
Mutualism
CommensalismIn commensalism: One species benefits and the other is not affectedDifficult to positively document in nature, because in any association between organisms both are probably affected
Cattle egrets and water buffalo
Interspecific Interactions and Adaptation
Evidence for coevolution– Which involves reciprocal genetic change by
interacting populations, is scarce
However, generalized adaptation of organisms to other organisms in their environment appears to be a fundamental feature of life
Species in the Structure of a Community
In general, a small number of species in a community exert strong control on that community’s structure.
Dominant and Keystone species (more on these soon)
Species Diversity
The species diversity of a community– Is the variety of different kinds of organisms that make
up the community– Has two components: species richness and relative
abundanceSpecies richness– Is the total number of different species in the
communityRelative abundance– Is the proportion each species represents of the total
individuals in the community
Two different communities can have the same species richness, but a different relative abundance
Community 1A: 25% B: 25% C: 25% D: 25%
Community 2A: 80% B: 5% C: 5% D: 10%
D
C
BA
A community with an even species abundance– Is more diverse than one in which one or two
species are abundant and the remainder rare
Trophic Structure
Trophic structure– Is the feeding relationships between organisms
in a community– Is a key factor in community dynamics
Food chains link the trophic levels from producers to top carnivores
Quaternary consumers
Tertiary consumers
Secondary consumers
Primary consumers
Primary producers
Carnivore
Carnivore
Carnivore
Herbivore
Plant
Carnivore
Carnivore
Carnivore
Zooplankton
Phytoplankton
A terrestrial food chain A marine food chain
Food Webs
A food web is a branching food chain with complex trophic interactions
Humans
Baleen whales
Crab-eater seals
Birds Fishes Squids
Leopardseals
Elephant seals
Smaller toothed whales
Sperm whales
Carnivorous plankton
Euphausids (krill)
Copepods
Phyto-plankton
Limits on Food Chain Length
Each food chain in a food web– Is usually only a few links long
There are two hypotheses that attempt to explain food chain length– The energetic hypothesis suggests that the
length of a food chain is limited by the inefficiency of energy transfer along the chain
– The dynamic stability hypothesis proposes that long food chains are less stable than short ones
Species with a Large Impact
Certain species have an especially large impact on the structure of entire communities– Either because they are highly abundant or
because they play a pivotal role in community dynamics
Dominant Species
Dominant species– Are those species in a community that are most
abundant or have the highest biomass– Exert powerful control over the occurrence and
distribution of other species
One hypothesis suggests that dominant species– Are most competitive in exploiting limited
resources
Another hypothesis for dominant species success– Is that they are most successful at avoiding
predators (human introduced invasive species as an example)
Keystone Species
Keystone species– Are not necessarily abundant in a community– Exert strong control on a community by their
ecological roles, or niches
Field studies of sea stars exhibit their role as a keystone species in intertidal communities
(a) The sea star Pisaster ochraceous feeds preferentially on mussels but will consume other invertebrates.
With Pisaster (control)
Without Pisaster (experimental)
Num
ber
of s
peci
es
pres
ent
0
5
10
15
20
1963 ´64 ´65 ´66 ´67 ´68 ´69 ´70 ´71 ´72 ´73
(b) When Pisaster was removed from an intertidal zone, mussels eventually took over the rock face and eliminated most other invertebrates and algae. In a control area from which Pisaster was not removed, there was little change in species diversity.
Observation of sea otter populations and their predation shows the effect the otters have on ocean communities
Food chain beforekiller whale involve-ment in chain
(a) Sea otter abundance
(b) Sea urchin biomass
(c) Total kelp density
Num
ber
per
0.25
m2
1972 1985 1989 1993 19970
2
468
10
0
100
200
300
400
Gra
ms
per
0.25
m2
Ott
er n
umbe
r (%
max
. co
unt)
0
40
20
60
80
100
Year
Food chain after killerwhales started preyingon otters
Ecosystem “Engineers” (Foundation Species)
Some organisms exert their influence– By causing physical changes in the
environment that affect community structure
Beaver dams can transform landscapes on a very large scale
Some foundation species act as facilitators– That have positive effects on the survival and
reproduction of some of the other species in the community
Salt marsh with Juncus (black rush) (foreground)
With Juncus
Without Juncus
Nu
mb
er
of
pla
nt
spe
cie
s
0
2
4
6
8
Conditions
Juncus slows salt buildup in soils and thereby increases species richness
Bottom-Up and Top-Down Controls
The bottom-up model of community organization– Proposes a unidirectional influence from
lower to higher trophic levels
In this case, the presence or absence of abiotic nutrients– Determines community structure, including
the abundance of primary producers
The top-down model of community organization– Proposes that control comes from the trophic
level above
In this case, predators control herbivores– Which in turn control primary producers
Disturbances
DisturbanceDisturbance influences species diversity and compositionA disturbance– Is an event that changes a community– Removes organisms from a community– Alters resource availability
Decades ago, most ecologists favored the traditional view that communities are in a state of equilibriumThe current view is a nonequilibrium model– Which describes communities as constantly changing
after being buffeted by disturbances
Fire– Is a significant disturbance in most terrestrial
ecosystems
– Is often a necessity in some communities
(a) Before a controlled burn.A prairie that has not burned forseveral years has a high propor-tion of detritus (dead grass).
(b) During the burn. The detritus serves as fuel for fires.
(c) After the burn. Approximately one month after the controlled burn, virtually all of the biomass in this prairie is living.
The intermediate disturbance hypothesis– Suggests that moderate levels of disturbance
can foster higher species diversity than low levels of disturbance
The large-scale fire in Yellowstone National Park in 1988– Demonstrated that communities can often
respond very rapidly to a massive disturbance
(a) Soon after fire. As this photo taken soon after the fire shows, the burn left a patchy landscape. Note the unburned trees in the distance.
(b) One year after fire. This photo of the same general area taken the following year indicates how rapidly the community began to recover. A variety of herbaceous plants, different from those in the former forest, cover the ground.
Human Disturbance
Humans are the most widespread agents of disturbance…no surprise there!
Human disturbance to communities– Usually reduces species diversity
Humans also prevent some naturally occurring disturbances which can be important to community structure (fire suppression)
Ecological Succession
Ecological succession– Is the sequence of community and ecosystem changes
after a disturbance
Primary succession– Occurs where no soil exists when succession begins
( as in a glacier retreat)
Secondary succession– Begins in an area where soil remains after a disturbance
( as in a post-fire forest)
Possible effects of early-arrivers
Early-arriving species– May facilitate the appearance of later species
by making the environment more favorable– May inhibit establishment of later species– May tolerate later species but have no impact
on their establishment
McBride glacier retreating
0 5 10
Miles
GlacierBay
Pleasant Is.
Johns HopkinsGl.
Reid Gl.
GrandPacific Gl.
Canada
Alaska
1940 1912
1899
1879
18791949
1879
1935
1760
17801830
1860
1913
1911
18921900
1879
1907 19481931
1941
1948
Cas
emen
t Gl.
McB
ride
Gl.
Plateau Gl.
Muir G
l.
Riggs G
l.
Retreating glaciers– Provide an opportunity to study succession
Glacier Bay, Alaska
Retreating glaciers leave behind rocky moraines
Succession on the moraines in Glacier Bay, Alaska follows a predictable pattern of change in vegetation and soil characteristics
The soil conditions change during succession as well
Species Diversity
Biogeographic factors affect community diversity
Two key factors correlated with a community’s species diversity– Are its geographic location and its size
Equatorial-Polar GradientsThe two key factors in equatorial-polar gradients of species richness
– evolutionary history – climate
Species richness generally declines along an equatorial-polar gradient (And is especially great in the tropics)
The greater age of tropical environments may account for the greater species richness.Polar and temperate areas have had to repeatedly “start-over” after big disturbances like glaciers.Climate is likely the primary cause of the latitudinal gradient in biodiversity due to differences in solar energy availability and water availability.
Area Effects
The species-area curve quantifies the idea that– All other factors being equal, the larger the
geographic area of a community, the greater the number of species
A species-area curve of North American breeding birds supports this idea
Area (acres)
1 10 100 103 104 105 106 107 108 109 1010
Nu
mb
er
of
spe
cie
s (lo
g s
cale
)
1
10
100
1,000
Island Equilibrium Model
Species richness on islands– Depends on island size, distance from the
mainland, immigration, and extinction
Studies of species richness on the Galápagos Islands– Support the prediction that species richness
increases with island size
The results of the study showed that plant species richness increased with island size, supporting the species-area theory.
FIELD STUDY
RESULTS
Ecologists Robert MacArthur and E. O. Wilson studied the number of plant species on the Galápagos Islands, which vary greatly in size, in relation to the area of each island.
CONCLUSION
200
100
50
25
10
0
Area of island (mi2) (log scale)
Num
ber
of p
lant
spe
cies
(lo
g sc
ale)
0.1 1 10 100 1,000
5
400
Community Structure
Two different views on community structure
The integrated hypothesis of community structure– Describes a community as an assemblage of closely
linked species, locked into association by mandatory biotic interactions
The individualistic hypothesis of community structure– Proposes that communities are loosely organized
associations of independently distributed species with the same abiotic requirements
Rivet and Redundancy Models
The rivet model of communities– Suggests that all species in a community are linked
together in a tight web of interactions– Also states that the loss of even a single species has
strong repercussions for the community
The redundancy model of communities– Proposes that if a species is lost from a community,
other species will fill the gap
Community hypotheses and models represent extremes, and that most communities probably lie somewhere in the middle