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Habitat Modeling

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Habitat Modeling. Goals. Predict the locations of as-yet undiscovered refuges in the Great Lakes Develop management protocols to create new unionid habitat. Goals. Predict the locations of as-yet undiscovered refuges in the Great Lakes - PowerPoint PPT Presentation
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Page 1: Habitat Modeling

Habitat Habitat ModelingModeling

Page 2: Habitat Modeling

GoalsGoalsPredict the locations of as-yet undiscovered refuges in the Great Lakes

Develop management protocols to create new unionid habitat

Page 3: Habitat Modeling

GoalsGoalsPredict the locations of as-yet undiscovered refuges in the Great Lakes

what habitat parameters are necessary to sustain unionid populations

develop a GIS-based model that will summarize all the important features of the refuges.

◦Test models predictions

◦Use an iterative process to refine the model.

Page 4: Habitat Modeling

Habitat parameters important for unionid protection from zebra mussels may include:

◦presence of substrates soft enough for unionids to burrow into

◦large areas of shallow waters (protected bayous) with low flow and warmer temperatures that encourage unionid burrowing

◦hydrological connection of the bayous to the lake

◦fish predation of Dreissena attached to unionids

◦Interactions of all these factors.

Page 5: Habitat Modeling

Factors that inhibit the establishment of stable dreissenid populations are:◦wave action in shallow areas, water

level fluctuations, ice scouring◦dense reed-beds◦remoteness from the source of

dreissenid veligers◦In addition, there may be other, yet

unidentified, mechanisms that promote the long-term coexistence of dreissenids and native mussels.

Page 6: Habitat Modeling

At the local scaleAt the local scaleFocus on areas inhabited by mussels:

◦substrate type, ◦depths, ◦water temperature, ◦water velocity◦location◦species richness and abundance.

Use multivariate methods such as multiscaled ordination with CCA (MSO-CCA) to define local scale habitat.

Page 7: Habitat Modeling
Page 8: Habitat Modeling

At a regional scaleAt a regional scaleUse ecological niche modeling to predict the

potential presence or absence of mussel beds. Lots of options for model types, GARP, SVM,

CART, etc. Use available environmental data

◦ water depth, wind-driven currents, mean, maximum and minimum annual temperature.

Developed GIS data layers ◦ Turbidity, distance to deep-water, bay area and

shape, bottom oxygen, distance to rivers, and human-related factors, such as distance to nearest dredging operation and distance to dams in upstream rivers.

Page 9: Habitat Modeling

Predicted the potential distribution of zebra mussels. Based on current distribution of zebra mussels in U.S. 11 geologic and environmental variables.

Biological model - 6 factors that have plausible explanations for limiting the distribution of zebra mussels. frost frequency, maximum annual temperature, elevation, slope,

bedrock geology, and surface geology.

No Elevation model

Drake & Bossenbroek, 2004, Bioscience

Ecological Niche ModelEcological Niche Model

Page 10: Habitat Modeling

Biological ModelBiological Model

0 500 1,000250

Kilometers¯

Biological Model

Value

100%

0%

ZMZebra MusselLocations

Predicted Distribution

Page 11: Habitat Modeling

0 500 1,000250

Kilometers¯

No Elevation

Value

High : 100

Low : 0

ZMZebra MusselLocations

Predicted Distribution

Biological Model minus Biological Model minus ElevationElevation

Page 12: Habitat Modeling

Support Vector Data Support Vector Data DescriptionDescriptionThe support vector data description

(SVDD) is an SVM for finding the boundary around a set of observations.

This boundary is the simplest boundary in the sense that it represents the smallest possible hyper- volume (a hypersphere) containing a specified fraction of the observations in the projected feature space

Page 13: Habitat Modeling

Support Vector Data Support Vector Data DescriptionDescription

Drake & Bossenbroek, 2009, Theor. Ecol.

Page 14: Habitat Modeling

Questions? Questions?


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