Lecture 12 Communities Flashcards

1
Q

Community ecology

A

Understanding dynamics/mechanisms of community structure & diversity is vital for conservation & management

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2
Q

Invasive species

A

E.g. lion fish Indo-Pacific native invaded coral reefs in Atlantic killing off native fish that consume algae causing algal overgrowth that impedes coral growth

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3
Q

Define a community

A

Group of interacting species occuring same place/time. Based on :
Taxonomy - related species
Guild - species using same resources
E.g. pollinators
Functional group - species w/same function not always using same resources e.g. legumes

Can describe communities in a single trophic level e.g. plants or multiple trophic levels

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4
Q

Food & interaction webs

A

Describe a community of species w/trophic & non-trophic interactions using good web/network

For specific trophic interactions describe community as network e.g. plant-pollinator network

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5
Q

Measuring communities

A

Patterns at scale of community often referred to as community structures

Captured by species diversity
2 components:

Species richness & abundance relative to other species (evenness)

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6
Q

Measuring communities: diversity: Shannon index

A

To calc Shannon index (H)
Natural log (ln) is applied to proportion (Pi) for each species (i) then multiplied by Pi again. All values are summed for all species in community and multiplied by -1 to get H

H= - sum of Pi+ln(Pi)

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7
Q

Measuring communities: similarities : Jaccard index

A

Community composition quantified/compared against other communities

E.g. surveying which bird species occur in two areas of forest

If 3 are unique to forest A and 3 to B and the two forests have 2 species in common then total no. Spp = 8 and 2/8=0.25 this is the Jaccard index

J=ab/(a+b+ab)

Jaccard index (J) measures special similarity/ species turnover from one site to another - part of beta diversity

More complex indices can account for species abundance in communities

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8
Q

How we end up with particular communities

A

Regional species pools & enviro filtering

1) dispersal sets limits by which species can arrive in a location
2) only species that survive to repro in abiotic conditions will persist
3)interactions w/other species determine final composition - biotic conditions

E.g. UK sycamore (Acer psuedoplatanus) failed to make it over the channel (we introduced it) before land bridge loss (dispersal filter)

Scots pine (Pinus sylvestris) extended to Britain ~9000 years ago declined in warmer climate and competition from broad leaf species (biotic/abiotic conditions)

Unique upper Teeside (Penines) calcerous soil leads to calcerous favouring plant assemblage (abiotic filter) cool wet climate (less competition than in low lands) arctic/ alpine species left behind since last glacial max. (Ice age)

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9
Q

Competition facilitation in plants

A

Major forces shaping communities

E.g. for plants: light/space/water/nutrients/ pollinators and disprrsers

Plant interactions may shift along altitudinal gradient from competition to facilitation

e.g. in low altitude plants compete w/neighbours with relative negative neighbour effect (neg RNE)

At higher altitudes plants benefit from neighbours that provide protection in harsh growing conditions - relative positive neighbour effect ( pos RNE)

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10
Q

Community dynamics: succession

A

Process of change in community over time

1) primary - occurs after catastrophic disturbances that kill all organisms leaving enviro devoid of life (or bare lifeless substrate w/no former community as in Petri dish agar)

2) secondary - started by event e.g. forest fire, harvest, hurricane that removed individuals/biomass of established species but not all life (especially soil remaining)

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11
Q

Succession example: glacier bay Alaska

A

Succession driven by interactions

As glacier melts (area becomes deglaciated)

1) moss and lichen develop soil substrate allowing germination and establishment of …
2) Dryas (flowering perennials) and shrubs add soil moisture, shelter and nutrients allowing establishment of…
3) Alder thicket - mutualistic bacteria in roots break down atmospheric N bonds fixing it into plant available N increasing growth of spruce species leading to ..
4) spruce forest w/dense shade, spruce outcompetes other species and becomes dominant

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12
Q

Interactions drive successions

A

N accumulation and soul formation is critical
Inhibitors at each stage reduce abundance of early colonisers due to competition

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13
Q

Primary succession

A

Driven by pathogens, diseases & herbivores also e.g. nematodes specific to marram grass drive succession of sand dune communities by limiting growth

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14
Q

Secondary succession

A

Cause is biotic or abiotic due to specific disturbance events or continuous removal of biomass e.g. 15 million trees blown down by great storm in 1987 or everyday herbivory of grazing cows

Can be viewed as disruption of initial primary succession - a ‘reset’

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15
Q

Disturbance as trigger for succession

A

Species can competitively exclude drivers in absence of disturbance

Disturbance by reducing abundance of dominant species can allow other species to persist

Known as intermediate disturbance hypothesis e.g. fire frequency - if too intense/frequent disturbance increases mortality so diversity declines. If too mild then dominant species cannot be competed with

Intermediate level of disturbance creates balance/diversity

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16
Q

Succession trajectories

A

Colonisation by diff species after disturbance can result in diff outcomes to succession - impeding it or speeding it up

E.g. Landslide prone Puerto Rican rainforest - ferns impede woody plant species preventing establishment of succession

17
Q

How can do many species survive in the rainforest?

A

Diff niches for competition avoidance e.g. diff rooting depths and diff flowering times

Neg density dependence

intraspecific competition greater than interspecific

Pathogens and herbivores prevent dominance of single plant species.