joe chipperfield department of biogeography
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Novel methods for the assessment of connectivity conservation in large-scale protected area networks. Joe Chipperfield Department of Biogeography. Connectivity. - PowerPoint PPT PresentationTRANSCRIPT
Novel methods for the assessment of connectivity conservation in large-scale
protected area networks
Joe ChipperfieldDepartment of Biogeography
Connectivity
• The term ‘connectivity’ is an attempt to assess the degree to which the spatial configuration of habitat interacts with a species dispersal abilities to hinder or promote the persistence of its populations residing within that habitat
• Two main subcategories:– Structural connectivity: Relates only to the spatial
configuration of patches– Functional connectivity: Includes biological
information in the calculation of connectivity
Structural versus Functional Connectivity
Structural Connectivity Functional Connectivity
Matrix
Calculation of Connectivity
Two stages required in the calculation of connectivity:
1. Determine your ‘patches’:– A priori determination– Determination through
assessment of species habitat preferences
2. Calculate the degree of potential patch utilisation within the network
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Scaling Up• These definitions of connectivity might not make sense when
scaling-up to larger spatial scales– Measurements made on ‘patch’ centroids or edges make
increasingly less sense– Functional responses based off small movement dynamics may not
scale to situations where the habitat patches are described in terms of spatial constructs with coarse resolution
• We already have methods available for assessing habitat suitability at macroecological scales in the form of species distribution models
• Is the concept of the patch still useful at macroecological scales?
Species Distribution Models
Output
Model
Observation Data
Environmental Data 1
Environmental Data 1
Environmental Data 1
• Inputs– Environmental
variables– Habitat
variables– Spatial filters
• Output– Probability of
Occurrence– Intensity
Problems with SDMs• The niche concept doesn’t actually map very well onto the output of a
SDM– Finding environmental covariates that describe distributional data is not quite
the same as calculating the niche of the species– We often treat observations as realisations of a species realised niche but then
project the model in a way that suggest we have derived the fundamental niche of a species
• The observation records are only partly dependant upon environmental covariates– Biotic interaction– Heterogeneity of sampling effort– Dispersal abilities– Habitat fidelity– Territoriality
Generate extra residual autocorrelation
Basic Model
• We start with a simple probit regression model:
c xp1
c: Intercept term
p: Vector of probabilities of occurrence
x: Matrix of covariates with each row holding the covariate values for a given location
β: Vector of regression coefficients
Probit Link Function: Inverse of the cumulative normal distribution function
Spatial Autoregression• To account for sources of extraneous autocorrelation we add an
autoregressive error term ϕ
• ϕ is a vector of random variables with values drawn from a Markov Random Field
• The vector has a correlation structure governed by two parameters:– τ: a parameter governing the magnitude of the deviations from zero– α: a parameter controlling the spatial dependency present in the Markov
Random Field• We also require a weights matrix that describes the neighbourhood
structure of the Markov random field
cxp1
Imperfect Detection• The observation of individuals across the species range is far
from perfect• We define two new types of error
– ɛ- : The probability of recording an ‘absence’ at a cell when the species really is present
– ɛ+ : The probability of recording a ‘presence’ at a cell when the species really is absent
• The simplest type of observation error simply assumes the following:
present species if-1absent species if
1-
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Relation to Niche Theory• The mapping to the concept of the ‘niche’ is still not
perfect using this method but is substantially improved compared to previous methods
Climate Only Prediction: Closer to the fundamental niche of the species
Full Prediction: Closer to the realised niche of the species
Neanderthal Distributions: Last Glacial Maximum
PLMMRF R Package
• The Probit Linear Model with Markov Random Fields has now been developed into an R package
• Look out for PLMMRF on CRAN soon• Interface is simple: very similar to the glm
function
gPLMMRF(observations ~ covar1 + covar2 + factor1 * factor2,autoweights = list(spatialWeightsMatrix, temporalWeightsMatrix),
obsModel = “binomial”, ...)
PLMMRF and Connectivity
• PLMMRF produces an occurrence map that takes into account non-climatic range determinants
• Unfortunately both the amount of occupied habitat in the reserve and the amount outside the reserve are random variables
• Develop a metric of ‘occupation conservation’:E(Proportion of occupied habitat in the reserve)
Further Extensions• The binary presence / absence case can be extended to the
case where the landscape can be classified into multiple types by changing the error function to a multinomial distribution and using a polychotomous link function
• New observation model possibilities– Allow for a linear observation submodel– Allow observation error to vary between landscape types and
sampler effort– Observation can have its own autoregressive component
• Interaction terms between spatial autoregression weight and covariates
Advantages• The model described here has many advantages over many
commonly applied species distribution models– Incorporates extraneous spatial (and even temporal)
autocorrelation– Incorporates observation uncertainty– Parameterised using Bayesian methods and so predictions take
into account uncertainty surrounding parameter values and predictions
– Model component are numerically tractable meaning that there is no need to rely on psuedo-likelihoods: autologistic regression
– Seperation of niche concepts in predictions• Connectivity defined on a much more appropriate scale
Acknowledgements
• Universität Trier: Stefan Lötters, Michael Veith, Katharina Filz, Jessica Weyer, Axel Hochkirch, Thomas Schmitt
• Universität Bonn: Dennis Rödder, Jan Engler
• University of York: Calvin Dytham, Chris Thomas
• Funding: Forschungsinitiative Rheinland-Pfalz Ministerium für Bildung, Wissenschaft, Jugend und Kultur