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Novel methods for the assessment of connectivity conservation in large- scale protected area networks 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 Presentation

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Page 1: Joe  Chipperfield Department of Biogeography

Novel methods for the assessment of connectivity conservation in large-scale

protected area networks

Joe ChipperfieldDepartment of Biogeography

Page 2: Joe  Chipperfield Department 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

Page 3: Joe  Chipperfield Department of Biogeography

Structural versus Functional Connectivity

Structural Connectivity Functional Connectivity

Matrix

Page 4: Joe  Chipperfield Department of Biogeography

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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Page 5: Joe  Chipperfield Department of Biogeography

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?

Page 6: Joe  Chipperfield Department of Biogeography

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

Page 7: Joe  Chipperfield Department of Biogeography

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

Page 8: Joe  Chipperfield Department of Biogeography

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

Page 9: Joe  Chipperfield Department of Biogeography

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

Page 10: Joe  Chipperfield Department of Biogeography

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-

iOP

Page 11: Joe  Chipperfield Department of Biogeography

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

Page 12: Joe  Chipperfield Department of Biogeography

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”, ...)

Page 13: Joe  Chipperfield Department of Biogeography

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)

Page 14: Joe  Chipperfield Department of Biogeography

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

Page 15: Joe  Chipperfield Department of Biogeography

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

Page 16: Joe  Chipperfield Department of Biogeography

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