habitat fragmentation (lecture 8) Flashcards

1
Q

How are naturally patchy habitats and habitats that have been fragmented by human activities different?

A

human fragmented landscape are typically

  • more fragmented
  • a harsher and more homogenous matrix
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2
Q

What’s the fragmentation process?

A
  • initially very small gaps form
  • little effect other than simple reductions in habitat quality
  • gaps get larger
  • fragments of habitat are isolated from eachother
  • impacts of fragmentation get worse with extent of fragmentation
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3
Q

How are habitat loss and fragmentation different?

A
  • lost habitat is always replaced by new habitat
  • fragmentation consists of habitat loss (& gain), smaller habitat patches, leading to isolated habitat patches surrounded by matrix
  • as more habitat is lost, impact becomes due to patch size and isolation (fragmentation) rather than the effect of habitat loss alone
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4
Q

What ecological principles relate to habitat fragmentation?

A
  • species-area relationships
  • island biogeography theory (IBT)
  • extinction debt
  • small population paradigm
  • edge effects
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5
Q

How do species-area relationships relate to habitat fragmentation?

A
  • more species in larger patches
  • bigger area = more micro habitats
  • bigger area = larger, more viable populations

e.g. rainforest butterflies fragmented by oil palm in Sabah (Benedick et al 2006) - species richness correlates with patch area size

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6
Q

What is island biogeography theory & how does it relate to habitat fragmentation?

A
  • MacArthur & Wilson, 1976
  • developed it to explain patterns of oceanic island species richness
  • balance between colonisation & extinction
  • relevant to habitat fragmentation if consider islands as patches, surrounding ocean as unsuitable habitat (matrix)
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7
Q

What does island biogeography theory predict?

A
  • colonisation rates are higher on islands close to mainland, decreases with number of species
  • extinction rates are higher on small islands, increases with number of species
  • number of species on an island at equilibrium of colonisation and extinction
  • continual turnover of species, some become
    extinct & others colonise
  • number of species eventually becomes constant.
  • loss of species, i.e. relaxation, if patches
    become smaller or more isolated
  • more species in large, less isolated patches
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8
Q

How does extinction debt relate to habitat fragmentation?

A
  • extinction debt is the idea that further extinctions will occur in a patch even without further change
  • 78% of related studies found evidence (Kuussaari et al., 2009)
  • sub-saharan african countries committed to losing 33% of forest primates due to past habitat loss
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9
Q

How does the small population paradigm relate to habitat fragmentation?

A
  • fragmentation increases number of small populations
    e. g. groups of black & gold howler monkeys in fragments have reduced genetic diversity compared to those in continuous forest (Oklander et al., 2010)
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10
Q

How do edge effects relate to habitat fragmentation?

A
  • greater relative impacts from external pressures in small fragments
    e. g. rainforest trees have higher mortality at patch edges
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11
Q

How does the matrix influence species response to fragmentation?

A
  • matrix quality influences species response

forest bird species in south africa (Neuschultz et al., 2011):
- greater decline in specialist species in natural forest fragment surrounded by eucalyptus plantation matrix than by agricultural matrix

  • IBT and species-area relationships assume species can’t survive in the matrix
  • matrix quality is crucial and predictions improve when taken into account
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12
Q

How does the species traits influence species response to fragmentation?

A

forest bird species in south africa (Neuschultz et al., 2011):
- generalist species barely declined

e. g. grassland butterflies differ in ability to disperse through the woodland matrix
- effects can vary hugely with subtle differences in matrix
- different butterfly species have different resistances e.g. to conifers vs willows

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13
Q

How can species maintain viable populations in single fragments?

A

likely in species with:

  • small home ranges
  • tolerant of edge effects

quantified by area sensitivity

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14
Q

How do species integrate multiple patches to survive?

A
  • integrate multiple patches into single home range
  • integrate multiple patches into a metapopulation
  • metapopulation = several smaller subpopulations linked together by recruitment of individuals into breeding population (gene flow)
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15
Q

How do metapopulations work?

A
  • not all fragmented populations are metapopulations: must be gene flow
  • source-sink dynamics: source generates recruits, sink only receives
  • most have habitat patches that aren’t constantly occupied but also crucial in ensuring overall viability
  • must consider when interpreting survey data
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16
Q

What precautions need to be taken when assessing fragmentation impacts?

A

crowding effect:

  • abundance spike as individuals move into available spaces
  • followed by density dependence and decline
    e. g. amazonian birds: crowding
    e. g. lumhlotz’s tree kangaroo is site faithful so no crowding

extinction debt:

  • determined by fragment size/isolation/species life span
  • extinction can be decades after fragmentation event
17
Q

How to design reserves to deal with fragmentation?

A
  • large
  • close to immigrant sources
  • shapes that minimise edge effects e.g circle is better than oval
  • in large patch, habitat variation and species richness may be increased in an elongation patch
18
Q

How to design corridors to deal with fragmentation?

A
  • linear or stepping stone
  • equal evidence for effectiveness of both

can have negative effect:

  • facilitate disease transmission
  • spread of exotic diseases
  • often implemented with little regard to potential conflict with humans, habitat selection and movement direction
19
Q

How to implement assisted movements to deal with fragmentation?

A
  • many large bodied species now confined to fragmented protected areas
  • most effective when combined with data on genetic diversity

BUT

  • costly & traumatic
  • is it a long term solution?