Community Ecology Flashcards
Ecological community
1) The small fraction of this enormous global collection of species that can be found at any particular place
Morin p. 3
Community ecology
1) The study of patterns and processes involving at least two species at a particular location
2) Can include predator-prey interactions and competition, things that are typically considered as part of population ecology
Morin p. 5
Population ecology
Focuses on patterns and processes involving single-species groups of individuals
Morin p. 5
Guild
Collection of species that use similar resources in similar ways Morin p. 6
Taxocene
Set of taxonomically related species within a community (e.g. birds, lizards, fish)
Morin p. 6
Functional group
A collection of species that are all engaged in some similar ecological process (often defined in arbitrary ways), e.g. primary producers
Morin p. 6
Trophic levels
Provides a way to recognize subsets of species within communities that acquire energy in similar ways (e.g. primary producers, herbivores, primary carnivores)
Morin p. 6
Food chains and food webs
Describe patterns of material and energy flow in communities, usually by diagramming the feeding links between consumer and the species that they consume
Morin p. 6
Ecosystems
Consist of one or more communities, together with abiotic surroundings
Morin p. 7
Ecosystem engineers
Species that physically alter the environment through their presence or behavior (e.g. beavers)
Morin p. 7
Four ways to delineate communities
1) Physically, by discrete habitat boundaries
2) Taxonomically, by the identity of a dominant indicator species
3) Interactively, by the existence of strong interactions among species
4) Statistically, by patterns of association among species
Morin p. 7
Physically-defined communities
Include assemblages of species found in a particular place or habitat (e.g. lakes, ponds, rotting fruits, whale falls OR forests into savannas into grasslands)
Morin p. 7
Biomes
1) Basic categories of communities that differ in their physical environments and in the life styles of their dominant organisms
2) 36 biomes
3) Global distribution of biomes is heavily influenced by precipitation and temperature
(Whittaker 1975)
Morin p. 7,9
Taxonomically-defined communities
Usually recognized by the presence of one or more conspicuous species that either dominate the community through sheer biomass, or otherwise contribute importantly to the physical attributes of the community (e.g. Redwood forests, beech-maple forests)
Morin p. 9
Statistically-defined communities
1) Consists of sets of species whose abundances are significantly correlated, positively or negatively, over space or time.
2) Species composition then has a geometrical interpretation as a directional vector, or arrow
Morin p. 9
Environmental gradient and abundance
ENTER FIG 1.3
Graphical representation of statistically-defined community
ENTER FIG 1.4
Interactively-defined community
Subsets of species in a particular place or habitat whose interactions significantly influence their abundances. Only some, and perhaps none, of the species in a physically defined community may constitute an interactively defined community.
E.g. Hairston (1981) used this approach to point out that only a small subset of the species of salamanders found in the mountains of North Carolina could be shown to interact and affect each other’s abundance.
Morin p. 14
Species richness
Total number of species present Ssub-t, May 1975
Synonymous with our most basic notions of biodiversity.
Morin p. 14
How to know if estimate of species richness is accurate?
1) Plot the cumulative number of species found against the amount of sampling effort. Beyond a certain amount of effort the species versus effort curve should reach an asymptote.
2) This asymptote provides a reasonable estimate of the number of species present.
3) Comparisons among communities that have been sampled with different amounts of effort can be made by using rarefaction curves
Morin p. 15
Shannon Index of Diversity
S= total number of species present
psubi = fraction of individuals in the sample that belong to species i
H prime = sum of all species (-psubi*ln(psubi))
Accounts for both number of species and distribution of species
Morin p. 15
Species evenness
J=Hprime/Hmax, or shannon diversity index over value of shannon diversity that would be obtained with an equal distribution
Morin p. 15
Simpson index of dominance or concentration
1) Expressed as the reciprocal of Simpson’s index, lambda
2) lambda = sum of all species (psubi^2) where psubi is the fraction of individuals in the sample that belong to species i
3) This is effectively the probability that any two individuals drawn at random from a sample will belong to the same species
4) So a high lambda (high probability of re-sampling the same individual) means a low Simpson index (1/lambda) means low diversity.
Morin p. 16
Alpha diversity
Local diversity within a single type of habitat (Whittaker 1975)
Morin p. 16
Beta diversity
Within a large geographic region, the turnover or change in species composition among different habitats (contributes to additional diversity)
Morin p. 16
Gamma diversity
Gamma diversity is related to alpha and beta diversity in that it equals the average alpha diversity among habitats plus the beta diversity within the region
Dsubg=avg(Dsuba) + Dsubb
Useful in determining if local diversity is determined largely by regional diversity or by local processes
Morin p. 16
Importance value of a species
1) Usually a measure of the fraction of total number of individuals or biomass in the sample accounted for each species plotted against the importance rank
2) Three common types are the broken-stick distribution, geometric series, and lognormal distribution
ENTER FIG 1.6
Morin p. 17
Predation and energy flow
(-/+), drives processes of energy and material flow up through food webs
Morin p. 19
Competition
(-/-) mutually negative
Morin p. 19
Amensalism
(0/-), one sided competitive interaction, where one species has a negative effect on another but the other has no detectable influence on the first
E.g. shading out one plant by another or allelopathy (inhibiting growth of one plant from the secretions of another)
Morin p. 19
Mutualism
(+/+), mutually positive interaction between a pair of species, where each has a positive effect on the other
E.g. oxpecker and zebra (food and pest control)
Morin p. 19
Commensalism
(0/+), one-sided mutualistic interaction, where one species has a positive effect on another species, but the second species has no net effect on the first
E.g. Remoras on sharks
Morin p. 19
Interspecific competition
(-/-), mutually negative interaction between two or more species within the same guild or trophic level. Can manifest in reduced abundance, decreased fitness, or a decrease in some fitness component such as body size, growth rate, fecundity, or survivorship.
Morin p. 24
How to study interspecific competition
Observational
1) Searching for negative correlations between the abundances of ecologically similar species
2) Using interspecific differences in morphology or resource use to infer possible competitive interactions (as evidence that species must differ by some fixed amount in order to avoid competitive exclusion)
Drawbacks: competition may not be the sole mechanism of these differences
Experimental
1) Manipulations of competitors in a lab or in a natural setting
Drawbacks: not always feasible or ethical, may not include other important ecosystem dynamics
Morin p. 25
Character displacement
Differences in morphology of ecologically similar species are greater in sympatry than in allopatry
Morin p. 25
Exploitation competition
Operates indirectly by the depletion of some shares resource (outdated term)
Morin p. 26
Interference competition
Involves direct interactions between species (outdated term)
Morin p. 26
Scramble competition
Usually involves resource utilization (outdated term)
Morin p. 26
Contest competition
Involves a behavioral interaction between species (outdated term)
Morin p. 26
Consumption (competition)
Happens when one species inhibits another by consuming a shared resource
E.g. competition between granivorous rodents and ants for seeds
Morin p. 26
Pre-emption (competition)
Occurs primarily between sessile organisms, Results when physical resource is occupied by one organism and made unavailable to others
E.g. rocky intertidal barnacles (settlement), encrusting bryozoans and corals.
Morin p. 26
Overgrowth (competition)
Does not require direct contact, only requires that growth of one species is inhibited by the growth of another
E.g. trees overshading one another and excluding shade intolerant species, encrusting bryozoans and corals.
Morin p. 26
Chemical interactions (allelopathy) (competition)
Chemical warfare between competitors
E.g. allelopathy in plants where one plant releases growth-inhibiting toxin that influences a nearby plant
Morin p. 26
Territoriality (competition)
Aggressive behavioral exclusion of organisms from specific units of space that are defended as territories.
E.g. brightly colored coral reef fish
Morin p. 26
Encounter competition
Results when non-territorial encounters between foraging individuals result in negative effects on one of both of the interacting individuals
E.g. laboratory studies of parasitoids foraging for prey, when two parasitoids encounter each other they may interact in ways that cause them to stop foraging, or to leave for a site where there may be more prey
Morin p. 27
Asymmetric competition
Most competition is asymmetric, with one species exerting control over another. Extreme cases can turn into amensalisms.
Morin p. 27
Descriptive models of interspecific competition
Describe how the abundance of one species affects the abundance of another, without specifically including a particular competitive mechanism
E.g. logistic model (adapted as the Lotka Volterra model)
Morin p. 27, 29
Mechanistic models of interspecific competition
Explicitly include information about the mechanism responsible for the effects of one species on another
Morin p. 28
Local stability (models)
If the population changes slightly will it return to a certain local equilibrium value
Morin p. 28
Global stability (models)
A system will return to the equilibrium point from any initial population value
Morin p. 28
Zero growth isoclines (models)
Equations for two lines that yield zero population growth for each species
Morin p. 30
Four possible competitive situations in Lotka Volterra model
1) unstable equilibrium, where K2>K1/alpha12 and K1>K2/alpha21
2) competitive exclusion of species 1 by species 2, where K2>K1/alpha12 and K1K2/alpha21
4) stable equilibrium where both species coexist K2
Priority effect (models)
Where initial conditions determine the outcome of an interaction
Morin p. 32
Non-additivity (models)
The existence of higher order interactions, when the pairwise effects of multiple competitive interactions (>2 species) cannot be added as the effect of one species on another depends on the complexity of the system
Morin p. 32
Liebig’s Law of the minimum
Where species require several resources to grow, growth rate will be determined by the resource in shortest supply
Morin p. 37
Neighboorhood models
How individual plants respond to variation in abundance of their immediate neighbors
Morin p. 40
Chaotic dynamics
When species abundance varies irregularly over time
Morin p. 39
Niche
1) No two species will be found to occupy the same niche
2) Implies that a competitive relationship between the species is important in affecting the ways in which species make their livings
3) Fundamental niche = where the species can persist
4) Realized niche = potential impact of other species in limiting the range of conditions successfully exploited by a given species
Grinnell (1914)
Morin p. 46
Competitive exclusion principle
Complete competitors cannot coexist, Hardin (1960)
Morin p. 46
Diffuse competition
No single species mat account for a large effect, but collectively, the impact of many species may be severe
Morin p. 47
Resource utilization niche
Focuses on consumable resources, or factors that serve as surrogates for those resources, such as different microhabitats
Morin p. 47
Niche complimentarity
Species that exhibit high overlap in habitat use, tend to have low overlap in food and vice versa
E.g. anolis lizards have a low overlap in structural habitat when there is a high overlap in prey size
Morin p. 49
Apparent competition
1) When the presence of multiple non-competing prey species elevates predator abundance above levels maintained by single prey species, which increases predation pressure on multiprey assemblages
2) E.g., Gastropods Tegula and Astraea do not compete with bivalves Chama and Mytilus, but their combined presence increases predator populations
3) E.g., Infestations of Pacific mites are more effectively controlled when Willamette mites are present as this increases predator abundance
Morin p. 51, 190-2
Replacement series model design
Used to show whether the per capita effects of interspecific competitors differ from those of intraspecific competitors, useful for frequecy-dependent competition
Morin p. 60
Example of interspecific competition in marine communities
1) Connell’s experiments on Chthamalus and Balanus
2) Chthamalus absence from Balanus zone coaused by competitive exclusion
Morin p. 63
Example of interspecific competition in marine plants
1) Dayton’s experiment on alga
2) The dominant alga in the lower intertidal zone had both negative competitive effects and positive effects on other alga species
3) The dominant alga would “shade out” other species and created favorable understory conditions for other species
Morin p. 65
Example of interspecific competition in terrestrial communities
1) Hairston’s experiments on terrestrial salamanders
2) Found results similar to Connell’s barnacle experiment with salamander and elevation
Morin p. 65
Asymmetric competition and predicting competitive ability
1) Competitive interactions are often strongly asymmetric
2) Asymmetry possibly due to differences in characteristic sizes of competitors, with larger predators having larger per capita impacts than smaller ones, OR differences in activity levels, which are probably correlated with rates of foraging and resource depletion
Morin p. 81
Overlap and interspecific competition
1) Hairston believed that high overlap yields weak competition and vice versa
Morin p. 65
Interphyletic competition
Competition amongst animals in different phyla, e.g. granivorous rodents and ants exploit seeds
Morin p. 83
Non-additive competition
1) In simple systems, aggregating the competitive effects of pairwise interactions between species is sufficient (additive interactions)
2) In more complex systems, per capita effects of interspecific competitors depend on the identity and density of other species in the system (non-additive or higher order interactions)
Morin p. 83
Predation in marine communities
1a) Paine and Pisaster
1b) Pisaster enhanced the number of species that managed to coexist in a limited area because they precent competitive exclusion
1c) Pisaster is a keystone species
2a) Lubchenco and Littorina
2b) Density of Littorina influenced the algae community
2c) For a predator to enhance the prey diversity, it must feed preferentially on the competitively dominant prey species
Morin p. 93-4
Predation in terrestrial communities
1) Tansley and Adamson’s grazing rabbits
2) Ungrazed plots showed successional changes
3) Herbaceous species naturally present in the grassland were maintained by rabbit grazing, and would be competitively excluded in the absence of grazing
Morin p. 97
Intraguild predation example
1) Lizards eat some spiders, but also compete with spiders for insects
2) When lizards are absent, there are a high number of insects, and plants develop insect defenses
2) When lizard are present there are fewer insects and plants do not develop defenses
Morin p. 101
Janzen-Connell hypothesis
1) Pathogens typically live close to plants
2) Seeds that disperse farther from the established parent will have a higher probability of survival because they will not be exposed to pathogens
Morin p. 103
Size-efficiency hypothesis
1) Brooks and Dodson and Hrbacek
2) Larger zooplankton are more efficient competitors
3) Small zooplankton cannot coexist with competitively superior large plankton
4) Planktivorous fish selectively consume larger zooplankton, releasing small zooplankton
5) Suggests that predators alter the size-structure and species composition of zooplankton assemblages
Morin p. 107
Can predators have negative effects on species richness?
1) Yes, for example pitcher plant mosquito larvae
2) Larvae consume protists, but protists do not have many competitors, so there was no release of other prey species when mosquitos were removed
Morin p. 107
Inducible defenses
1) Defenses only produced in response to predator cues
2) Daphnia produce spines when predators are present
3) Due to phenotypic plasticity
Morin p. 110
Constitutive defenses
1) If the risk of predation is high and constant, prey produce permanent defenses
Morin p. 110
Errington’s hypothesis
1) Predators often have little actual impact on total prey abundance because they are consuming prey that could not secure safe territories or refuges from predators
2) Assumes that prey populations are ultimately regulated by competition among prey for predator-free sites
Morin p. 111
HSS hypothesis
1) Herbivores are surrounded by a surplus of food, so herbivores are not limited by competition
2) Detractors: chemical defenses of plants, plant specialists
3) Objection to detractors: at least one species will be able to eat another species of toxic plant
Morin p. 111-2
Fretwell’s extension of HSS
1) In even numbered food chains, herbivores are limited by competition
2) In odd numbered food chains, herbivores are limited by predation
Morin p. 113