Ecological community Flashcards

1
Q

Ecological communities

A

A community is a group of potentially interacting species that occur together in space and time

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2
Q

bioregions

A
  • communities can be defined by plants occurring there/ The endemic species of each area are low but different in relative abundance and dominat is the main driver.
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3
Q

key processes in ecological communities

A

-Selection = changes in community structure caused by non-random(“deterministic”) fitness differences between taxa
Selection pressure:
• Varies over space / time
• Constant
• Density-dependent
-Drift is random changes in the relative abundances of different taxa within the community through time“Neutral processes”
-Diversification is the evolution of new lineages (including new genotypes, forms, varieties, sub-species and species) from existing lineages
-Dispersal is the movement of individuals from one place to another, as propagules (seeds and spores), larvae, juveniles or adults
• Immigrating \ emigrating
• Source \ receiver
• One-way (large to small)
• Linking local communities

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4
Q

explain the current diversity of Australian plant communities

A

Persistence of rainforest species that evolved prior to the breakup of Gondwana.
Persistence of species that evolved after the breakup of Gondwana in response to a trend of drying of the continent and increased frequency of fire.
Dispersal of rainforest species from SE Asia into Australia.

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5
Q

different form of diversity

A

⍺ diversity : the composition of a local ecological community with respect to its richness (number of species), evenness (distribution of abundances of the species), or both
ß diversity : the extent of change in community composition, or degree of community differentiation, across a region.

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6
Q

Shannon index

A
S = total number species
Pi = proportion for i th species
H = Shannon diversity index
Hmax = maximum possible H if individuals completely evenly distributed among species
H= -(Sum of Pi x lnPi)
Equality= J= H/lnS
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7
Q

Simpson’s index

A
S = total number species
Pi = proportion for i
th species
D = Simpson’s index
1-(Sum of P square)
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8
Q

Problem with measuring diversity

A
  • detectability of species ( some species are hard to detect the present) and even if detection is possible. The richness is unknown. or it’s only possible to measure the possibility of the present. in that case, the sum of the probability is the species richness
  • Taxon, many species are still unknown so hard to determine species present
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9
Q

G.E.Hutchinson fundamental niche

A

Niche of a species is a multidimensional hyperspace, containing conditions and resources that allow the species to survive

  • condition are aspect of the environment that are not affected by consumtion
  • resources are aspect of the environment that become less abundant as it is being consume
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10
Q

Realised niche

A
the actual niche that a species are found in is smaller - reasons include:
• Competition
• Dispersal limitations
• Disturbances
• Stochasticity
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11
Q

Environmental gradients

A
- Variation in the condition and resources of the environment
• Cover
• Aspect
• Solar radiation
• Temperature
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12
Q

Environmental variables

A

Terrestrial Climate: annual precipitation, minimum temperature of coldest period;
temperature seasonality, potential evapotranspiration; humidity or vapour
pressure deficit; solar radiation adjusted for topography; snow cover; frostfree days; topographic: slope roughness (variation); soil: type, depth, water
holding capacity
Freshwater Variables characterising upstream (catchment), local watershed, riparian
zone and downstream conditions, including flow magnitude and variability,
frequency of flood and drought events, temperature, water quality (N, P),
streambed conditions (bedrock type, surface complexity, substrate particle
size)
Marine Depth, seabed topographic features, temperature, salinity, dissolved
oxygen, currents, productivity (e.g. chlorophyll-a)

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13
Q

How are communites shaped based on their interaction

A
  1. Competitive exclusion
  2. Resource partitioning
    Spatial and temporal variability allows co-existence
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14
Q

Competitive exclusion

A

If two species compete for the same limited resource, one will dominate in the long term
the growth of two species of Paramecium when cultured separately and together. The P.aurelia out compete the P.caudatum

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15
Q

Resource partitioning

A

-species change morphology (size and shape) to reduce competition = character displacement
Mud snails, Hydrobia, two species change size when they are in a same community even though they have similar when they are separates
-species change behaviour
golden spiny mouse and common spiny mouse, both are nocturnal but when together , golden become diurnal

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16
Q

Measuring community patterns in space

A

Objective methods
Based on data
Pattern analysis
• association (how similar they are via cluster analysis and bray-curtis similar scale)
• classification (examining the composition of species at sites. those that have the same species are pooled together into a class. then, predict the effect of present or absence of those species in the comunity
• ordination (difference in condition and resources)

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17
Q

Mapping a distibution of species

A
  • look at a community in regard to their environment
    -define a community that occur in an area
    -model base on measurement
    -map it out the community to their enviroment
    Two steps: classify the organism there, then predict the map
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18
Q

interspecific interactions

A
Community interactions are classified by whether they help, harm, or have no effect on the species involved
\+/+ mutualism
\+/0 comenialism
-/- competition
\+/- paratism or predatism
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19
Q

Parasites

A
  • Smaller than host
  • Live on or in host for extended time
  • Usually don’t kill host
  • Host may recover from parasite
  • The habitats of parasites are themselves alive
  • Grow
  • Respond
  • Evolve
  • Move
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20
Q

Abundant of parasites

A
• Protozoans
• Animals
• Fungi
• Plants
Relative abundance of different taxa, and proportion of parasitic species in those taxa
Host species > 1 parasite
the total biomass of parasites often equalling or exceeding the biomass of some tropic
 levels.
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21
Q

Predation

A

Feeding of one organism on another
• Predators
• Animals that capture and eat other animals
• Herbivores
• Animals that consume plants / plant parts

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22
Q

Keystone predator

A

A keystone predator has such an important role in the community that it helps to define the community. If it is removed, the community will be drastically different, or cease to exist

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23
Q

Indirect effects of predation

A
  • Developmental, morphological, physiological, behavioural
  • Significant costs
  • Meta-analysis = systematic analysis of results of published research
  • clear evidence that the impact of intimidation on prey demographics was at least as strong as direct consumption
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24
Q

example of Indirect effects of predation

A

Nursery web sipder
• Forest in Connecticut, USA
• Hiding: 18% reduction in daily activity
time
• Change of diet: 70% grass if no spider;
42% grass if spider

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25
Q

Impact spatial arrangements

A
  • Finland forest bird community
  • Sparrowhawk (predator)
  • Predation risk closest to nest
  • Birds of preferred prey size avoided nests
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26
Q

Herbivory & Australian vegetation

A
Native herbivores:
• wombat, kangaroos, bettongs, possums…
• grasshoppers, beetles, termites..
Introduced:
• Cattle, goats, camels, deer, rabbits..
Change composition and structure
Increase cover
Increase exotic weeds
Decrease plant species richess
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27
Q

Trophic level

A

τροφή (trophē) - food or nourishment
Food chain
Food web
Summarises trophic relationship

28
Q

Food webs in saltmarsh communities

A

• Parasites affect food webs, so should be included.
• Parasites are difficult to include due to difficulties in studying
(tiny, hard to detect, hard to identify etc)
• Subwebs: predator-prey, parasite-host, predator-parasite, parasite-parasite.
• Topological food web: focus on number and distribution of connections, using data

29
Q

Trophic cascades

A

= predator –prey effects that alter the abundance, biomass or productivity of a species, functional group or trophic level across more than one link in a food web
Top -down control
Bottom -up control

30
Q

Predator and prey cycle

A

The predator and prey cycle occurs because the predator population increases in response to the increase prey population. The growing predator population begins to suppress the prey population, which declines, and the predator population then declines as it food source declines. The predation then allows the prey to increase again, starting a new cycle
.

31
Q

different scales of interspecies interaction

A
nterspecific interactions are 
important across many different scales
• Time (temporal scales)
• Space (geographic scales)
• Body size (morphometric scales)
32
Q

Temporal scales

A
  • Earliest known insect pollination of a flower
  • Cretaceous period (99 million years ago)
  • Tumbling flower beetle, eudicot pollen
  • Cane toads in Australia
  • Novel predator‐prey interactions
  • Sand goannas are naïve to bufotoxin
  • Trophic cascades?
33
Q

Geographical scales

A

Bogong moth
• Larval stage: plains of NSW & QLD
• Adults: migrate > 1,000 km to the alpine zone
• Important food species for mountain pygmy possum

34
Q

Morphometric scales

A

Humpback whale (16,000 mm; 30,000,000 g) feed on Antarctic krill (60 mm; 2 g)

35
Q

effect of co evolution

A

: Co‐evolution drives beneficial & antagonistic relationships between species
Mutualistic relationships (+/+) are common in many ecological communities
• These relationships are the result of co‐ evolution: when unrelated organisms evolve in a coordinated fashion
• Mutualistic relationships can be specific (between 2 species) or diffuse (between groups of species)

36
Q

Mycorrhizae: Plants & fungi

A
  • Fungi supply water and nutrients (e.g., N and P) to plants
  • Plants supply products of photosynthesis (sugars) to fungi
  • Plants show increased resistance to pathogens
  • Global association: present in ~80% of plant species
  • Common mycorrhizal networks transmit water, nutrients, information between plants
  • Multiple plants are linked belowground
  • Communication via biochemical signals changes plant behaviour
  • Root growth, shoot growth, photosynthetic rate, foliar nutrition and defence responses
37
Q

Flying‐foxes and plants

A
  • Mutualistic relationship between mammalian herbivores (flying‐foxes) and many species of plants
  • Flying‐foxes feed on nectar, blossom and fruits
  • Important pollinators and seed dispersers in Australia and the Pacific
  • Declining flying‐fox populations may impact many species in a community
  • Flying‐foxes are becoming more urban
38
Q

Coral and zooxanthellae

A
  • Mutualistic relationship between coral polyps (animals) and single‐celled dinoflagellates (algae)
  • Zooxanthellae live within the coral: ≤30,000 algal cells/mm 3 of coral tissue
  • Coral reefs depend on this relationship
  • When stressed, coral may expel their zooxanthellae, leading to coral bleaching
  • Bleaching events are becoming more common as ocean temperatures rise
39
Q

Newts and garter snakes

A
  • Newts of the genus Taricha (prey) produce tetrodotoxin (TTX), a powerful neurotoxin
  • Garter snakes (predator) have evolved resistance to tetrodotoxin
  • Resistance is not uniform across space: geographic hotspots & coldspots of co‐ evolution
  • Selection drives variation in resistance
40
Q

effect of Disruption of inter‐specific

interactions

A

Disruption of inter‐specific interactions can alter communities
• Inter‐specific interactions, developed over time via co‐evolution, can shape ecological communities
• Disruption of important interactions can alter ecological communities
• This includes changes to species composition and community structure

41
Q

Potoroos, truffles and

mycorrhizae

A
  • Small mammals in the family Potoroidae feed on truffles (underground fruiting bodies of mycorrhizal fungi)
  • Important disperser of spores – ‘ecosystem engineers’
  • High extinction rate of small mammals in Australia, many species threatened
42
Q

Flying‐foxes and plants on

Christmas Island

A
  • The CI flying‐fox is the last surviving endemic mammal on Christmas Island
  • One of two frugivores – important seed disperser & pollinator
  • Critically endangered following significant population declines
  • Impacts on native plants and vegetation structure?
43
Q

Ecological communities are

constantly changing

A
  • Communities are never static
  • Changes are linked to the four community‐level processes
  • Selection, dispersal and drift are important over shorter time scales (years to centuries)
  • Evolutionary diversification may be less important over these time scales
44
Q

Succession in vegetation communities

A
  • Succession: natural changes in the composition and structure of an ecological community over time
  • The replacement of one community by another
  • Orderly succession?
45
Q

Vegetation succession

at Wilsons Promontory

A
  • Yanakie Isthmus at Wilsons Promontory
  • Vegetation changes 1958 to 2008
  • Invasion of Coastal grassy woodland by coastal tea‐tree Leptospermum laevigatum
  • Management of fire and grazing to restore woodland
46
Q

Stylised
succession in
six stages

A
  1. Bare rock
  2. Mosses & grasses
  3. Grasses & perennials
  4. Woody pioneers
  5. Fast‐growing
    trees
  6. ‘Climax’ forest
47
Q

Disturbance can drive changes in

ecological communities

A
  • Disturbance: a discrete event that disrupts the structure of an ecological community, changing resource availability and/or the physical environment
  • Natural disturbances include bushfires, floods, cyclones, volcanic activity, disease
  • Human‐generated disturbances include habitat clearing, urban development, pollution
48
Q

Effects of disturbance

A
  • Changed environmental conditions may favour different species to those present prior to the disturbance – selection
  • They may allow new species to move in via dispersal
  • Disturbance can also have random effects on community composition – drift
49
Q

Disturbance regimes

A
  • Regime: the long‐term pattern of disturbance across a landscape – its frequency, size and intensity
  • Disturbance regimes as probabilities: how likely is a disturbance event of a particular size and intensity in a given year/decade?
  • Estimated using historical data
  • Changes to disturbance regimes can be considered as a threatening process
  • E.g., bushfires likely to become more frequent and more intense in south‐east Australia under climate change
  • Long‐term changes in the composition of communities that are burnt too frequently
50
Q

Invasive species alter community

composition and structure

A
  • Invasion by feral (non‐native) species is a threatening process in ecological communities around the world
  • Invasive species can alter community structure and composition in dramatic ways
  • Invasive species affect terrestrial, freshwater & marine communities
51
Q

Feral predators in Australia

A

• Predation by cats and foxes threatens many species of mammals, birds & reptiles
• Each is listed as a threatening process
• Cats kill > 1 million animals per day
• ‘The war on cats’
• Impacts on ecological communities?
• Body size and habitat influence
vulnerability to predation

52
Q

Probability of a bird species being preyed upon by a cat vs key predictor variables

A

Habitat (G = grassland, SH =
shrubland/heathland, OF = woodland/open forest, RF = rainforest/ mangrove X, FW = freshwater X, CM = coastal/marine)
-bird that weight form 60-400g are more likely to be eaten by feral cat

53
Q

Feral herbivores in Australia

A
  • Rabbits, horses, camels, deer, goats…
  • Change vegetation through grazing and trampling
  • Cause soil erosion, damage waterways
  • Impact on the habitat of many other species
  • Control of feral herbivores is difficult and often controversial
54
Q

Ecological communities can be

an effective target for conservation

A
  • Many conservation efforts are focused on individual species
  • Ecological communities can also be a target for conservation
  • Each approach has benefits and limitation
55
Q

Conservation of single species

A
• Benefits:
o A tangible target
o Conceptually simple
o Charismatic species can engage 
people with nature conservation
• Limitations:
o Expensive
o Risky
o Problem of conserving a species 
that has no viable habitat
56
Q

Conservation of ecological communities

A

• Benefits:
o Can target many species at the same time
o More efficient use of resources
o Captures non‐charismatic species and important inter‐specific relationships
• Limitations:
o Requires protection of land/space
o Communities can be subject to multiple threats

57
Q

Banksia Woodlands of the Swan Coastal Plain

A
  • Listed as an endangered ecological community in 2016
  • Part of the SW Western Australia biodiversity hotspot
  • Very diverse: 600+ plant species, and animal species
  • Supports 20+ threatened species
  • Faces a range of threats
58
Q

Banksia Woodlands of the Swan Coastal Plain

Facing a range of threats:

A
• Habitat clearing for agriculture and 
urban development
• Mining
• Habitat fragmentation
• Phytophthora dieback – from an 
introduced fungal pathogen
• Invasive species
• Climate change
59
Q

EPBC Act

A
  • The EPBC Act is Australia’s federal conservation legislation
  • Provides a legal framework to protect and manage matters of national environmental significance (MNES)
  • MNES include threatened species, migratory species and threatened ecological communities
60
Q

The EPBC Act effectiveness

A

• Ineffective – species continue to decline, clearing of threatened ecological communities is rarely prevented
• Samuel Review is currently underway:
• “Australia’s natural environment and iconic places are in an overall state of decline and
are under increasing threat”
• Recommending new national standards & an independent environmental regulator

61
Q

Giant kelp marine forests of south‐east Australia:

Endangered (2012)

A
  • Giant kelp Macrocystis pyrifera forms a closed canopy
  • The largest and fastest growing marine plant, favours cold water
  • Adds vertical structure, creating habitat for many other species
  • Threats: climate change (sea‐surface temperature, weather patterns), increased nutrient availability
62
Q
Lowland rainforest of subtropical Australia: 
Critically Endangered (2011)
A
  • Tall closed forest
  • Diverse community including many species of plants, animals & fungi
  • Previously one of Australia’s largest rainforests
  • Extensively cleared for timber and agriculture/grazing
  • Ongoing clearing for horticulture & residential development
63
Q

Managing threats to ecological

communities is difficult but important

A
  • To conserve ecological communities more effectively, we need to manage the threats they face
  • How do we best do this?
  • Stronger legislation, more research, more funding for management?
  • Recognising that conservation problems have a social as well as an ecological aspect
64
Q

Natural temperate grassland of the Victorian

Volcanic Plain: Critically Endangered

A
  • < 0.1% of pre‐European extent remaining
  • Community includes many threatened species
  • Faces a variety of threats:
  • urban development
  • invasive species (weeds)
  • changed disturbance regimes
65
Q

Melbourne Strategic Assessment 2009

A
  • Conducted under the EPBC Act
  • 40,000 ha of new housing
  • 4,500 ha of grassland to be lost
  • New grassland reserves to be established as an “offset” (15000) ha
  • Some provisions for EPBC‐listed species incl. growling grass frog
66
Q

What went wrong Melbourne Strategic Assessment 2009

A
  • Offsets trade off a definite loss versus a possible future gain
  • The new grassland reserves have not been delivered
  • New wetlands to compensate for lost growling grass frog habitat are not yet built
  • Better EPBC compliance & enforcement required
67
Q

Structure classification

A