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Quantifying Patterns of Biological Diversity using Vertebrate Habitat Models

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Title: Quantifying Patterns of Biological Diversity using Vertebrate Habitat Models


1
Quantifying Patterns of Biological Diversity
using Vertebrate Habitat Models
  • Frank A. La Sorte

2
Acknowledgements
  • Southwest Regional Gap Analysis Project Bruce
    C. Thompson, Kenneth G. Boykin, Scott Schrader,
    Robert A. Deitner.
  • New Mexico Cooperative Fish and Wildlife Research
    Unit, New Mexico State University.

3
Justification
  • We require tools to quantify large scale patterns
    of biological diversity
  • provide information for decision making on large
    scale environmental issues
  • Adequately documenting these patterns is
    inherently difficult
  • tremendous ecological complexity
  • lack of time and resources

4
Justification (continued)
  • Trade off
  • document large scale patterns quickly with
    limited precision, accuracy, generality, and
    predictability
  • Gap analysis presents regional patterns of
    vertebrate habitat associations within their
    estimated ranges
  • However, it lacks well defined methods for
  • quantifying diversity
  • decision making

5
Objectives
  • Concept of Ecological Diversity
  • Dimensions and Components
  • Quantifying Diversity Patterns within Gap
    Analysis
  • Richness, Evenness, Distinctness
  • Example 1996 New Mexico Gap Data
  • New Mexico
  • Tularosa Basin
  • Applications for Decision Making

6
Limitations
  • Models are subjective, non-probabilistic, and
    static
  • Accuracy unknown
  • Level of error propagation unknown
  • Variables highly correlated
  • Qualitative (presence/absence)
  • Limited to vertebrates
  • Varying perceptions of scale by species
  • Habitat is scale dependent
  • No intra- and interspecific factors
  • Ignores size and spatial arrangement of patches

7
Ecological Diversity
  • Units
  • Grain
  • Extent
  • Diversity patterns
  • Richness
  • Evenness
  • Taxonomic distinctness
  • Landscape patterns
  • Time

8
Diversity Patterns
9
Vertebrate Habitat Models
  • Large scale biological and abiotic features, that
    can be represented cartographically, found within
    the estimated range of a species
  • Combined with Boolean AND operators to create a
    binary grid (presence/absence)

10
Gap Richness
  • Definition quantity of vertebrate habitats
    within a unit area
  • Sum all vertebrate habitat models

11
Richness
  • Does not predict presence, persistence, fitness,
    habitat quality, or biodiversity
  • Interpretation of richness hotspots problematic
  • Not consistent across taxa
  • Scale dependent
  • Biased towards marginal populations

12
Gap Evenness
  • Definition How evenly vertebrate habitat is
    distributed within a taxonomic level in a unit
    area
  • Species as the unit of evenness
  • Summarize evenness trend with principle component
    analysis

13
Evenness Metrics
  • Non-ordered or scalar metrics
  • Ordered metrics
  • Information theory (Rényi, Hill)
  • Cumulative measures (Lorenz curve)

14
Lorenz Curve
Lorenz Curve (0, 0) (1/s, p1) (2/s, p1
p2)(s-1/s, p1 p2 ps-1) (1, 1) Where the
proportions are ranked p1lt p2ltlt ps for s
groups Gini Coefficient (Area between the
Lorenz Curve and the line of equality) x 2
15
Lorenz Curve
16
Gap Taxonomic Distinctness
  • Definition How taxonomically distinct vertebrate
    habitat is within a unit area
  • Measured as the average taxonomic path length for
    each cell based upon a weighting factor (Clarke
    Warwick 1998)
  • Path length weights (?)

Average path length
17
Example New Mexico
  • NM GAP 1996
  • 100 x 100 m cells
  • 346 vertebrate species
  • 20 Orders
  • 55 Families
  • 195 Genera

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22
Example Tularosa Basin
Alamogordo
White Sands National Monument
Sacramento Mountains
9,369.2 km2
23
Richness
Taxonomic distinctness
Evenness
Order
Family
24
Correlation Matrix
25
Application to decision making
  • Provides more detailed information on the
    patterns of diversity
  • multivariate nature of diversity
  • Use a combination of diversity components with
    other variables to
  • more accurately represent gaps
  • contrast sites based upon some criteria
  • locate sites with desired characteristics

26
Decision Making
  • Assist in directing policy, research, management,
    and conservation efforts more efficiently
  • Should not be the sole source of information
  • Should be interpreted cautiously and honestly
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