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Habitat Fragmentation

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Most landscapes are made up of discreet patches, depending on scale ... Results in inbreeding depression. Reduced fitness because of breeding with related individuals ... – PowerPoint PPT presentation

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Title: Habitat Fragmentation


1
Chapter 7
  • Habitat Fragmentation

2
What is a fragment?
3
Habitat Fragmentation
  • Disruption of large, continuous blocks of habitat
    into less continuous habitat
  • Two components
  • Reduction in area
  • Change in habitat configuration
  • Results in small, isolated natural areas among
    human settlements/activities

4
Figure 7.1 in book adapted from Curtis 1956.
5
Heterogeneity
  • Most landscapes are made up of discreet patches,
    depending on scale
  • Natural patchiness, or mosaics
  • Differences due to
  • Vegetation
  • Soil type
  • Elevation
  • Microclimate effects of the above

6
Metapopulations
  • Systems of local population linked by occasional
    dispersal
  • Requires patches are somehow accessible
  • Persistence can not occur if patches are not
    connected
  • Corridors, stepping stones, or other habitat for
    dispersal

7
Is fragmentation good?
  • What is the difference between natural patchiness
    andhuman-induced fragmentation?

8
Natural vs. Human Fragments
  • Still a popular area of investigation for
    ecologists and conservation biologists
  • Can land management mimic natural patchiness?
  • Some generalizations possible

9
Hypotheses
  • Fragmentation results in reduction of the extent
    and connectivity of habitats.

10
Hypotheses
  • Rich vs. simple patch structure

11
Hypotheses
  • Natural patchiness has less contrast and
    less-intense edge effects than fragments.

12
Hypotheses
  • Aspects of human-induced fragmentation pose
    additional threats to populations.

13
Natural vs. Human Fragments
  • Human-induced fragmentation creates different
    landscape and patchiness
  • The degree of difference from natural landscape
    affects the degree of threat

14
Process of Fragmentation
  • Graduate process whereby the fragments become the
    matrix
  • Matrix the most common habitat type

15
Process of Fragmentation
  • Loss of biological integrity is unknown
  • Many factors contribute to effects of
    fragmentation
  • Site fidelity
  • Degree of mobility
  • Delayed spatio-temporal effects

16
Biological Consequences
  • Initial exclusion
  • Crowding effect
  • Insularization and area effects
  • Isolation
  • Edge effects
  • Matrix effects
  • Roads
  • Species invasions
  • Ecological process

17
Initial exclusion
  • Elimination of species that only occurred in the
    portion of landscape destroyed
  • Esp. important for endemic species, or narrowly
    distributed species
  • Movement to another area of suitable habitat is
    one way to avoid this

18
Crowding Effect
  • Increase of individuals in an area of suitable
    habitat AFTER other portions have been destroyed
  • Displacement results in initial population
    increase
  • Not necessarily healthy population incr.
  • Population crash quickly follows

19
Crowding Effect
  • Demonstrated in Brazil (Bierrgaard and Lovejoy
    1989)
  • Natural patches fragments of varying sizes
    surveyed for birds
  • SLOSS single large or several small
  • Many factors affecting the answer to this
    question, some species/area dependent

20
Bierrgaard and Lovejoy 1989
21
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22
Insularization and area effects
  • Formation of island habitats
  • Number of species declines as area available
    declines
  • Protected areas may not be large enough

23
Insularization and area effects
  • Area sensitive species
  • Species who seem to require more area than their
    home range/territory size would suggest
  • Extinction of species increases as area decreases
  • Particularly as the surrounding matrix changes,
    or becomes less suitable

24
Isolation
  • Occurs when habitat patch becomes increasingly
    surrounded by unsuitable habitat
  • Vast expanses of unsuitable habitat form
    barriers to movement
  • Results in inbreeding depression
  • Reduced fitness because of breeding with related
    individuals

25
Edge effects
  • The boundary of a fragment is not a line, but a
    zone of influence
  • Edge sealing in warmer climates
  • Edge poses an ecological trap for some species

26
Edge effects
  • Edge of the habitat is of poorer quality than the
    interior (core) of the fragment

27
Matrix effects
  • Matrix most common habitat type
  • Structural contrast between fragments and
    surrounding matrix
  • Similar matrix effects
  • May provide marginal habitat
  • Facilitates movement among fragments

28
Matrix effects
  • Movement among fragments decreases as
    matrix-fragment structure differs
  • Strong implications for intensity of edge effects

29
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30
Roads
  • Often ignored source of fragmentation
  • Considerations for conservation
  • Mortality from road construction and collision
  • Alteration of physical and chemical environments
  • Spread of invasive species
  • Increased potential for human interaction

31
Roads
  • Barriers to movements of many species

32
Roads
  • Hazards pose disproportionate threat for sex
    classes of some species
  • Roads offer means of dispersal for invasive
    species

33
Species invasions
  • Use roads, power lines as corridors to new
    habitat fragments
  • Results in increased species richness, although
    native species may suffer

34
Effects on ecological processes
  • Microclimate influences rates of nutrient
    cycling, decomposition
  • Pollination rates vary with isolation or
    connectivity of fragments
  • Ecosystems maintained by regular disturbance
    (fire) negatively impacted by fragmentation

35
Biological Consequences
  • Initial exclusion
  • Crowding effect
  • Insularization and area effects
  • Isolation
  • Edge effects
  • Matrix effects
  • Roads
  • Species invasions
  • Ecological process

36
Species Vulnerable to Fragmentation
  • Wide-ranging species
  • Not simply sum of total fragment area
  • Nonvagile species
  • Low dispersal ability
  • Specialized requirements
  • Particular resource requirements
  • Reliance on ephemeral habitats/resources

37
Species Vulnerable to Fragmentation
  • Large-patch or interior species
  • Less likely to move through unsuitable habitat
  • Low fecundity or recruitment
  • Low reproductive capacity
  • Value to humans
  • Hunting/trapping species with high economic value
  • Movement between fragments increases potential
    for harvest

38
Climate Change and Fragmentation
  • Both threats may pose a synergistic threat to
    biodiversity
  • Threats to migratory species
  • High elevation habitats may be lost

39
How to counter effects of fragmentation?
40
Connectivity
  • The movement and genetic interchange of species
    such that viability is enhanced
  • Ideally, conservation of largest tracts of
    habitat should be conserved
  • Corridors, stepping stones, and other management
    tools to promote movement

41
Yellowstone to Yukon
  • Effort to maintain connectivity of mountainous
    region in westernNorth America
  • http//maps.y2y.net/googlemap.htm

42
Additional Recommendations
  • Avoid further fragmentation/patch isolation
  • Utilize buffer zones
  • Consider matrix structure
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