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Biodiversity at local scales

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Patterns of commonness and rarity are scale-dependent and may shift over time ... Gaps in temperate and tropical forests are important in maintaining diversity ... – PowerPoint PPT presentation

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Title: Biodiversity at local scales


1
Biodiversity at local scales
  • Reading assignment GSF Ch. 13

2
Biodiversity at Local Scales
  • Differing abundances of different species may
    result from variable competitive ability
    (fitness) among species, or from stochastic
    factors
  • Patterns of commonness and rarity are
    scale-dependent and may shift over time
  • Common species are called dominants
  • Most species are not common

3
Three aspects of species distributions
(Rabinowitz, 1981)
  • Geographic range (wide/narrow)
  • Habitat specificity (broad/restricted)
  • Local abundance (somewhere large vs. everywhere
    small)

4
Why are species common?
  • Ecological generalists wide habitat tolerance
    broad fundamental niches
  • Common species are superior organisms, more
    competitive for resources
  • This theory has been partially supported, but
    maybe common species happen to be well adapted to
    commonly found environmental conditions

5
Why are species rare?
  • Classic explanation is that species tend to be
    ecologically specialized
  • Low abundance
  • Small geographic ranges (endemism)
  • Rare species can efficiently exploit their
    specialized niche
  • Lack of dispersal (spatial and temporal barriers)
  • Historical accidents

6
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7
Why are species invasive?
  • Invasive species are those that expand their
    ranges rapidly outside their native habitat
  • May be weedy or ruderal but not always
  • May be native to the region but more often exotic
  • Community and ecosystem properties may be altered
  • Most invasive species have been introduced by
    people (2000-3000 species in US, last 100 years)

8
Traits of Invasive Species (also see Mack et
al., 2000)
  • Invaders have a variety of strategies for
    spreading
  • Lots of seeds, wind dispersal
  • Rhizomes
  • For pines, reproduction at a young age, small
    seeds and large, frequent seed crops
  • Rapid growth lack of natural predators/pathogens
  • Empty niches
  • Invaders may alter ecosystem properties in a way
    that increases their success (feedback)

9
Diffuse knapweed
10
Novel Weapons hypothesis(Callaway and Ridenour)
  • Certain root exudates are ineffective against
    natural neighbors
  • Diffuse knapweed (Centaurea diffusa) produces
    8-hydroxyquinoline, an allelopathic compound that
    has adverse effects on many plants outside its
    native range
  • Selective advantage may result in rapid evolution
    of the weapon
  • Competitive ability is further strengthened

11
Testing Allelopathy
Root exudates collected from diffuse knapweed
inhibited shoot and root differentiation and
germination of native plant seedlings, crop
plants and even other invasive species
Vivanco et al. 2004
12
Identifying allelopathic compounds
  • Allelopathic compound is less concentrated in
    soils of knapweeds native range than in invaded
    soils

Vivanco et al. 2004
13
And to make matters even worse
  • Plants exposed to root boring insects for
    biological control produce more allelopathic
    chemicals, reduce native grass growth more
  • Biocontrol actually makes these plants more
    competitive

Thelen et al. 2005
14
Ecosystem Conditions leading to Invasion
  • Empty niches (Elton 1958)
  • Species-poor communities have more ecological
    space for invaders
  • Evidence is mixed!
  • Unused resources
  • Dalmation toadflax, tap-rooted perennial forb,
    invades mixed grass prairie few other species
    make use of deep soil moisture
  • Disturbance
  • Increases resource availability and niche space

15
What is the role of empty niches in invasion?
  • Dominant paradigm says that species-poor areas
    are susceptible to invasion
  • Species-rich communities may have higher rate of
    invasive species (Fig. 13.5)
  • S. African fynbos, New Zealand beech forests, and
    Great Plains grasslands show similar patterns
  • Are species-rich areas more fertile?

16
  • What is the role of disturbance in invasion?
  • More work needs to be done on specific mechanisms
    driving disturbance-invasion cycles
  • Factors promoting likelihood of invasion after
    disturbance
  • soil surface conditions, microclimate
  • water infiltration rates
  • competition
  • natural enemies
  • resource (nutrient) availability
  • feedbacks kochia and cheatgrass increase N
    cycling rates

17
Phases of invasion
  • Lag phase many introduced species disappear
  • Population increases slowly
  • Often multiple introductions of the same species
    occur over time and space
  • Invasion phase rapid population increase in
    number and area
  • Eventually the population and area stabilizes
    (may take centuries)
  • The tens idea

18
Phases of invasion
Mack et al. 2000
19
Scales of Diversity(see Table 15.4)
  • Inventory diversity (species density,
    Shannon-Weiner index, etc)
  • Alpha diversity within one community
  • Gamma diversity across several communities
  • Differentiation diversity (mean similarity,
    turnover)
  • Beta diversity difference in community
    composition along an environmental gradient or
    among communities in landscape
  • See coenocline slide

20
Why do some areas have high species diversity?
  • As productivity (or resources, or area)
    increases, the number of species should, too
  • Assumes that more productivity is driven by more
    energy in the system, which would support more
    individuals (or species)
  • Paradox of Enrichment at high productivity,
    some individuals (species) outcompete others if
    they get bigger or take up more space, leading to
    lower diversity

21
The relationship between productivity and
diversity is very scale dependent
22
Productivity-Diversity Patterns Highest
biodiversity was found at intermediate levels of
productivity in 40 of studies Could be that
areas with intermediate productivity and
fertility are most common, and more species are
adapted to these conditions
23
Does disturbance promote diversity?
  • Gaps in temperate and tropical forests are
    important in maintaining diversity
  • Stochastic events lead to species coexistence
  • Intermediate disturbance hypothesis
  • Competitive exclusion reduces diversity at low
    levels of disturbance
  • Recolonization may be too slow at high levels of
    disturbance
  • Recent review showed marginal support for this
    idea (Fig. 13.10)

24
Does increased biodiversity increase
productivity? (why might this happen?)
  • Much of the increased productivity was associated
    with functional groups
  • May be dependent on particular species

25
Does increased biodiversity increase ecosystem
stability?
  • What is stability?
  • If stability is reduced variability, there is
    some evidence for a relationship (Fig. 13.12)

26
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