Ecology Quiz 7 Flashcards

1
Q

What are communities? Definition

In practical terms, ecologists usually define communities based on: (can’t study all of communities bc there are too many so must split it up)

A

Communities: are groups of interacting species that occur together at the same place and time.
So far we have considered species interactions in two way relationships. In reality, species experience multiple interactions that shape the communities in which they live.

Physical characteristics: e.g., all species in a sand dune, mountain stream.

Biological characteristics: e.g., all the species associated with a kelp forest or a coral reef; implies importance of abundant species.

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2
Q

Ecologists usually consider a subset of species when they define and study communities.
Subsets can be defined by:

A
  1. Taxonomic affinity: Example: a study might be confined to all bird species in a community
  2. Guild: groups of species that use the same resources.
  3. Functional group: species that function in similar ways, but do not necessarily use the same resources.
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3
Q

Community structure:

A

Community structure: Set of characteristics that shape communities. Provides a basis for generating hypotheses and experiments to understand how communities work.

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4
Q

Community structure is usually characterized by:

A
  1. Species diversity
    Species diversity combines species richness and species evenness
  2. Species composition (identities of species in community)
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5
Q
  1. Species diversity

How do ecologists determine when most or all of the species in a community have been observed?

A

Species diversity combines species richness and species evenness

Species richness: the total number of species in a community.

Question? Species accumulation curves: Species richness plotted as a function of total number of individuals counted. The threshold where no new species are counted never occurs in natural systems because new species are constantly being found.

Species evenness: (horizontal) (proportion of species in a given community) Describing relative abundance - Rank abundance curves plot the proportional abundance of each species (pi ) relative to the others, in rank order.

Suggests possible species interactions:

E.g dominant species might have a strong negative effect on less abundant species.

Rank-abundance curves for four closed-canopy tree communities spanning a large latitudinal gradient, from boreal to equatorial Amazonian forest (after Hubbell 1996).

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6
Q

The most commonly used species diversity index is the Shannon index: species richness and evenness

Equation

A

pi = proportion of individuals in the ith species - abundance/total - higher pi means more diverse based on advance and evenness - mor evenness will give you higher diversity pi number
s = number of species in the community

H= - S Pi ln (Pi)

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7
Q
  1. Species composition
A

Species composition: the identities of species present in the community. Two communities could have identical species diversity values but have completely different species.

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8
Q

Species diversity VS Biodiversity VS Environmental complexity

A

Species diversity = the number of species in a community.

Biodiversity describes diversity at multiple spatial scales, from genes to species to communities. Implicit is the interconnectedness of all the components. - genes all the way to ecosystem

Environmental complexity: In general, species diversity increases with environmental complexity or heterogeneity.
Robert MacArthur found warbler diversity increased as vegetation stature increased.
Many studies have shown a positive relationship between environmental complexity and species diversity.

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9
Q

Interactions of Multiple Species:

Buss and Jackson (1979) hypothesized that competitive networks allow the

A

Interactions of Multiple Species: Communities can be characterized by complex networks of direct and indirect interactions varying in strength and direction - More than two species! –> Competitive networks: Interactions among multiple species in which every species has a negative effect on every other species.

May be hundreds of species within a community.
Many, indirect interactions.
Many types of interactions (competition, predation, mutualism).

Buss and Jackson (1979) hypothesized that competitive networks allow the coexistence of competitors and maintain species richness.

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10
Q

Test of the competitive network hypothesis:

A

Algae and invertebrate species compete for space on coral reefs by overgrowing one another.

In areas of overlap, researchers determined the proportion of wins (species on top) to losses (species on bottom).

No species won consistently. species interacted in a circular network rather than a linear hierarchy.

Results support the idea that competitive networks, by fostering diffuse and indirect interactions, promote diversity in communities

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11
Q

Trophic cascade:

A

Trophic cascade: how nature is organized - indirect positive interaction - keystone

Rate of consumption at one trophic level results in change in species abundance or composition at lower trophic levels:
- A carnivore eats an herbivore (a direct negative effect on the herbivore).
- The decrease in herbivore abundance has a positive effect on a primary producer.
- Indirect effects in interaction webs.

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12
Q

Foundation versus Keystone Species

A

Foundation species have large effects on other species, and thus species diversity, by virtue of their considerable abundance and biomass, e.g., trees, corals.

Some dominant species are ecosystem engineers: they create, modify, or maintain physical habitat for themselves and other species.

Keystone species have a low relative abundance and biomass, but a strong effect on other species, despite their rarity and low biomass.

Keystone Species: Large effect, disproportionate to their biomass or abundance.

Beavers: Keystone Species and Ecosystem Engineers - Wetlands increased with beaver recovery, and regional biodiversity increases

Some species play only a small role in community structure and function:
Contribute to overall diversity and their presence or absence has little significance for the ultimate regulation of the community
Some might be redundant bc they have similar functions as other species but might be important bc redundant can help when species are disturbed

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13
Q

Theory of succession:

Factors -

Primary and Secondary

A

Change in species composition in communities over time, resulting from both biotic and abiotic factors. Succession involves colonization and extinction due to abiotic and biotic agents of change. Although climax communities are assumed to be the endpoint of ecological succession, some believe that there is no such thing… that a community never actually reaches a climax! - succession theory comes from plants bc sessile.

Abiotic agents of change fall into two categories:
Disturbance: Events that injure or kill some individuals and create opportunities for other individuals, e.g., tsunami.
Stress: Abiotic factors that reduce growth, reproduction, or survival of individuals, e.g., increasing temperature.

Biotic agents of change:
Species interactions can result in species replacements
Diseases can cause death or slow growth of a species.
Ecosystem engineers or keystone species can influence community change.

Primary succession: Starts off with no life and progress to climax stage

Secondary succession: Either in an intermediate or climax stage and then some disturbance where you have to start off from scratch

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14
Q

Spectrum of disturbance:

Clements:

Gleason:

A

Spectrum of disturbance:
Agents of change vary in frequency and intensity.

Clements:
Community has a predictable life history
Ultimately reaches a stable end point called the “climax community.
Climax communities have dominant species that persist over many years and provide stability
Superorganism

Gleason:
“Individualist concept” that succession is the result of environmental requirements of the individual species
He also noted that “. . . no two species make identical environmental demands.”
Succession reflected the interactions of individuals with the environment

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15
Q

Henry Cowles:

A

Henry Cowles: Studied succession on sand dunes along Lake Michigan. - replacing time with space and observe succession without having to wait for hundreds of years

Plant assemblages farthest from the lake’s edge were the oldest;

Plants nearest the lake were the youngest,

Representing a time series of successional stages.

“Succession was a variable chasing a variable” – the changes in vegetation chase the changes in the climate.

Predict how communities would change over time without actually waiting for the pattern to unfold (“space for time substitution”)

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16
Q

Connell and Slatyer (1977) reviewed the literature on succession and proposed three mechanisms:

A
  1. Facilitation - Clements - Superorganism
  2. Tolerance - Gleason
  3. Inhibition

Facilitation model - inspired by Clements. Early species modify the environment in ways that benefit later species. The sequence of species facilitations leads to a climax community

Tolerance model - also assumes the earliest species modify the environment, but in neutral ways that neither benefit nor inhibit later species

Inhibition model - assumes early species modify conditions in negative ways that hinder later successional species

17
Q

Basics of succession

A

Facilitation model, inspired by Clements—early species modify the environment in ways that benefit later species.

The sequence of species facilitations leads to a climax community.

Balanus facilitates macroalgae by reducing limpet grazing

Inhibition model—assumes early species modify conditions in negative ways that hinder later successional species (e.g. Algal succession on Southern California Boulders).

18
Q

Primary succession

A

Starts off with no life from scratch and progress to climax stage
Substrate that has never been colonized before starting from “scratch”
Primary succession: Colonization of habitats devoid of life (e.g volcanic rock - lava brand new no life).
Parent material tend to be a lichen(algae-autotroph and fungi-body - symbiosis in mutualism) which is nitrogen fixing
Life forms differ in the timing of changes during primary succession
Melting glaciers - sequence of communities reflecting succession over many centuries (early stages of primary succession seen further inland - experiment called a natural experiment when substituting space for time)
Elapsed time from exposure: 0-10 years - Community: lichens, mosses, horsetail, liverwort
The first colonizers (pioneer or early successional species) tend to be stress-tolerant.
Elapsed time from exposure: 0-45 years - Community: willow, alder (Alnus), Dryas, cottonwood
Elapsed time from exposure: 45-70 years - Community: Alder (Alnus) thicket [nitrogen fixaCon]
Elapsed time from exposure: 70-115 years - Forest transition: less alder, more sitka spruce (Picea)
Elapsed time from exposure: 115-200 years - Community: sitka spruce (Picea sitchensis) forest
Elapsed time from exposure: 200 plus years - Community: Western hemlock (Tsuga heterophylla)
Plant species diversity increases over time for succession
Richness estimated over 1500 years, increases then levels off
Early little time and over time get more species
Soils change during primary succession
Soil organic matter, moisture, and nitrogen concentration increased as succession progressed

19
Q

Secondary succession

A

Either in an intermediate or climax stage and then some disturbance where you have to start off from scratch
Reestablishment of community after disturbance or destruction of previous
Fire, human activity, natural disasters
Progressive succession
Leads to communities that are more complex, more biomass, more species

20
Q

Succession in animal communities

A

Some trends in interspecific differences can be explained by:
Particular ecological traits such as tolerance to harsh microclimates, breeding requirements, and other habitat associations.
Species that are more resistant to desiccation and species with high thermal tolerances and metabolic rates can tolerate recently disturbed habitats that have high solar irradiation and warm, dry microclimatic conditions.

21
Q

Limitations of Theories:

A

Experimental studies: succession is driven by multiple mechanisms. No one model fits one community
In nature, even an old, seemingly stable community is in a state of flux and is a shifting mosaic rather than a steady state.
Succession is not always predictable and unidirectional.
A major limitation for our understanding of forest succession is the short time usually available for its study, relative to the generally longer time span over which the process takes place (decades/centuries).
Cedar creek example (Clark et al 2019)
Divergent successional trajectories in the herbaceous community after 88 years of old-field succession.
Changes due to contingent (non-random) factors such as site conditions, competition, and demographic trade-offs rather than stochastic (random) factors.

22
Q

Alternative stable states

A

Communities can follow different successional paths and display alternative states.
Different stable communities may develop in the same area under similar environmental conditions
A community is stable when it returns to its original state after perturbation (resilience) or shows resistance to that perturbation.
A visual model of alternative stable states - Hysteresis is an inability to shift back to the original community type, even when original conditions are restored.

An example of an alternative stable state -
John Sutherland studied two types of communities developed on the tiles over time, one dominated by Styela and another by Schizoporella.
Different communities developed depending on whether the tiles were protected from fish predation.