Title: Quantifying Patterns of Biological Diversity using Vertebrate Habitat Models
1Quantifying Patterns of Biological Diversity
using Vertebrate Habitat Models
2Acknowledgements
- 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.
3Justification
- 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
4Justification (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
5Objectives
- 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
6Limitations
- 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
7Ecological Diversity
- Units
- Grain
- Extent
- Diversity patterns
- Richness
- Evenness
- Taxonomic distinctness
- Landscape patterns
- Time
8Diversity Patterns
9Vertebrate 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)
10Gap Richness
- Definition quantity of vertebrate habitats
within a unit area - Sum all vertebrate habitat models
11Richness
- 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
12Gap 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
13Evenness Metrics
- Non-ordered or scalar metrics
- Ordered metrics
- Information theory (Rényi, Hill)
- Cumulative measures (Lorenz curve)
14Lorenz 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
15Lorenz Curve
16Gap 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)
Average path length
17Example New Mexico
- NM GAP 1996
- 100 x 100 m cells
- 346 vertebrate species
- 20 Orders
- 55 Families
- 195 Genera
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22Example Tularosa Basin
Alamogordo
White Sands National Monument
Sacramento Mountains
9,369.2 km2
23Richness
Taxonomic distinctness
Evenness
Order
Family
24Correlation Matrix
25Application 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
26Decision 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