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Lecture #4: Lecture #4: Bayesian analysis Bayesian analysis of mapped data of mapped data Spatial statistics in practice Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical Garden Tunghai University & Fushan Botanical Garden

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Page 1: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Lecture #4:Lecture #4: Bayesian Bayesian analysis of analysis of

mapped datamapped data

Spatial statistics in Spatial statistics in practicepractice

Center for Tropical Ecology and Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Biodiversity, Tunghai University & Fushan

Botanical GardenBotanical Garden

Page 2: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Topics for today’s lecture

• Frequentist versus Bayesian perspectives.

• Implementing random effects models in GeoBUGS.

• Spatially structured and unstructured random effects: the CAR, the ICAR, and the spatial filter specifications

Page 3: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

LMM & GLMM move in the direction of Bayesian modeling

• Fixed effects are in keeping with a frequentist viewpoint―individual unknown parameters

• Random effects are distributions of parameters, and are in keeping with a Bayesian viewpoint

• The model specifications tend to be the same, with estimation methods tending to differ

Page 4: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Sampling distribution-based inference: the reported p values

• Frequentism: assigns probabilities to random events only according to their relative frequencies of occurrence, rejecting degree-of-belief interpretations of mathematical probability theory.

• The frequentist approach considers to be an unknown constant. Allowing for the possibility that can take on a range of values, frequentist inference is based on a hypothetical repeated sampling principle that obtains desirable and (often) physically interpretable properties (e.g., CIs).

• Frequentist statistics typically is limited to posing questions in terms of a null hypothesis (i.e., H0) that a parameter takes on a single value.

Page 5: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

What is Bayesian analysis?

• Bayesianism: contends that mathematical probability theory pertains to degree of plausibility/belief; when used with Bayes theorem (which casts analysis in conditional terms), it becomes Bayesian inference.

• The Bayesian approach considers as the realized value of a random variable Θ with a probability density (mass) function called the prior distribution (a marginal probability distribution that is interpreted as a description of what is known about a variable in the absence of empirical/theoretical evidence).

• Bayesian statistics furnishes a generic tool for inferring model parameter probability distribution functions from data: a parameter has a distribution, not a single value.

Page 6: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

• The Bayesian interpretation of probability allows (proper prior) probabilities to be assigned subjectively to random events, in accordance with a researcher’s beliefs.

• Proper prior: a probability distribution that is normalized to one, and asymptotically dominated by the likelihood function

– improper prior: a handy analytic form (such as a constant or logarithmic distribution) that, when integrated over a parameter space, tends to 1 and so is not normalizable.

• Noninformative prior: because no prior information is available, the selected prior contains vague/general information about a parameter, having minimal influence on inferences.

Page 7: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

• conjugate prior: a prior probability distribution naturally connected with the likelihood function that, when combined with the likelihood and normalized, produces a posterior probability distribution that is of the same type as the prior, making the analytical mathematics of integration easy. (NOTE: MCMC techniques relaxes the need for this type of specification)

• The hierarchical Bayes model is called “hierarchical” because it has two levels. At the higher level, hyper-parameter distributions are described by multivariate priors. Such distributions are characterized by vectors of means and covariance matrices; spatial autocorrelation is captured here. At the lower level, individuals’ behavior is described by probabilities of achieving some outcome that are governed by a particular model specification.

Page 8: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

• posterior distribution: a conditional probability distribution for a parameter taking empirical evidence into account computed with Bayes’ theorem as a normalized product of the likelihood function and the prior distributions that supports Bayesian inference about the parameter

• Bayesian statistics assumes that the probability distribution in question is known, and hence involves integration to get the normalizing constant. This integration might be tricky, and in many cases there is no analytical solution. With the advent of computers and various integration techniques, this problem can partially be overcome. In many Bayesian statistics applications a prior is tabulated and then sophisticated numerical integration techniques (e.g., MCMC) are used to derive posterior distributions.

Page 9: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

The controversy

• A frequentist generally has no objection to the use of the Bayes formula, but when prior probabilities are lacking s/he deplores the Bayesians’ tendency to make them up out of thin air.

• Does a parameter have one or many values?

• For many (but not all) of the simpler problems where frequentist methodology seems to give satisfying answers, the Bayesian approach yields basically the same answers, provided noninformative proper priors are used.

Page 10: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Frequentist Bayesian

Definition of probability

Long-run expected frequency in repeated (actual or hypothetical) experiments (Law of LN)

Relative degree of belief in the state of the world

Point estimate

Maximum likelihood estimate

Mean, mode or median of the posterior probability distribution

Confidence intervals for parameters

Based on the Likelihood Ratio Test (LRT) i.e., the expected probability distribution of the maximum likelihood estimate over many experiments

“credible intervals” based on the posterior probability distribution

Page 11: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Confidence intervals of non-parameters

Based on likelihood profile/LRT, or by resampling from the sampling distribution of the parameter

Calculated directly from the distribution of parameters

Model selection

Discard terms that are not significantly different from a nested (null) model at a previously set confidence level

Retain terms in models, on the argument that processes are not absent simply because they are not statistically significant

Difficulties Confidence intervals are confusing (range that will contain the true value in a proportion α of repeated experiments); rejection of model terms for “non-significance”

Subjectivity; need to specify priors

Page 12: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Impact of sample size

priordistribution likelihood

distribution

As the sample size increases, a prior distri-bution has less and less impact on results; BUT

effectivesample sizefor spatially

autocorrelateddata

Page 13: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

What is BUGS?

Bayesian inference Using Gibbs Sampling

• is a piece of computer software for the Bayesian analysis of complex statistical models using Markov chain Monte Carlo (MCMC) methods.

• It grew from a statistical research project at the MRC BIOSTATISTICAL UNIT in Cambridge, but now is developed jointly with the Imperial College School of Medicine at St Mary’s, London.

Page 14: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

• The Classic BUGS program uses text-based model description and a command-line interface, and versions are available for major computer platforms (e.g., Sparc, Dos). However, it is not being further developed.

BUGS

Classic BUGS

WinBUGS (Windows Version)

GeoBUGS (spatial models)

PKBUGS (pharmokinetic modelling)

Page 15: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

What is WinBUGS?

• WinBUGS, a windows program with an option of a graphical user interface, the standard ‘point-and-click’ windows interface, and on-line monitoring and convergence diagnostics. It also supports Batch-mode running (version 1.4).

• GeoBUGS, an add-on to WinBUGS that fits spatial models and produces a range of maps as output.

• PKBUGS, an efficient and user-friendly interface for specifying complex population pharmacokinetic and pharmacodynamic (PK/PD) models within the WinBUGS software.

Page 16: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

What is GeoBUGS?• Available via

http://www.mrc-bsu.cam.ac.uk/ bugs/winbugs/geobugs.shtml

• Bayesian inference is used to spatially smooth the standardized incidence ratios using Markov chain Monte Carlo (MCMC) methods. GeoBUGS implements models for data that are collected within discrete regions (not at the individual level), and smoothing is done based on Markov random field models for the neighborhood structure of the regions relative to each other.

Page 17: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Choice of Priors

• Can effect – model convergence – execution speed– computational overflow errors

• Consider– Conjugate prior– Sensible prior for the range of a parameter

• e.g. Poisson mean must be positive; hence, a normal distribution is not a good prior.

– Truncated Prior• useful if it is known that sensible or useful parameter

values are within a particular range

Page 18: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Parameter Initialization

• Initialize important parameters.– Parameters distributed according to a non-

informative prior must be initialized (otherwise an overflow error is very likely).

• Regions are numbered sequentially from 1 to n

• Each region is defined as a polygon in a map file

• Each region is associated with a unique index

• BUGs can import map files from Arcinfo, Epimap, SPLUS.

GeoBUGs

Page 19: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Review: What is MCMCMCMC?

MCMC is used to simulate from some distribution p known only up to a constant

factor, C:

pi = Cqi

where qi is known but C is unknown and too horrible to calculate.

MCMC begins with conditional (marginal) distributions, and MCMC sampling outputs a sample of parameters drawn from their joint

(posterior) distribution.

Page 20: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

GeoBugs: spatial Poisson with a map

model;{for (i in 1:M){ for (j in 1:N){

#Poisson with a constant but unknown mean

y[i,j] ~ dpois(l)

#GeoBUGS numbers regions in a sequence#This statement turns a 2-D array into a 1-D array for GeoBUGS

mapy[j + (i-1)N] <- y[I,j]}

}

#priors#Noninformative conjugate priors for Poisson mean.

l~dgamma(0.001,0.001)}

Page 21: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Displaying a map with GeoBugs

• Compile model, load data, load initial conditions

• Set sample monitor on desired variables

• Set trace

• Set sample monitor on map variable OR set summary monitor on map variable

• Run chain

• Activate map tool, load appropriate map

• Set cut points, colour spectrum as desired.

Page 22: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Poisson mixture on a spatial lattice

model;{for (i in 1:M){

for (j in 1:N){y[i,j] ~ dpois(l[i,j])l[i,j] <- mu1*x[i,j]+ (1-x[i,j])*mu2x[i,j] ~ dbin(p,1)

#These statements are for the benefit of GeoBugsmapx[j + (i-1)*N] <- x[i,j]mapy[j + (i-1)*N] <- y[i,j]mapl[j+(i-1)*N] <-l[i,j]

}}

#priorsp~dunif(0,1)

#Noninformative conjugate priors for Poisson means.mu1~dgamma(0.001,0.001)mu2~dgamma(0.001,0.001)}

Poisson mean varies

x[i,j] in (0,1)

x[i,j] independent binomials

Map the hidden latticeand the Poisson means

E(mu) = /; var(mu) =

Page 23: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Introducing a covariatemodel;{for (i in 1:M){

for (j in 1:N){y[i,j] ~ dpois(l[i,j])l[i,j] <- mu1*x[i,j]+ (1-x[i,j])*mu2[i,j]log(mu2[i,j])<-cov[i,j]*beta2x[i,j] ~ dbin(p,1)

#These statements are for the benefit of GeoBugsmapx[j + (i-1)*N] <- x[i,j]mapy[j + (i-1)*N] <- y[i,j]mapl[j+(i-1)*N] <-l[i,j]

}}

#priorsp~dunif(0,1)mu1~dgamma(0.001,0.001)beta2~dnorm(0,0.001)}

Poisson mean varies with location

Log link function

Normal prior for covariate parameter

Page 24: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Adding a random effect

model;{for (i in 1:M){

for (j in 1:N){y[i,j] ~ dpois(l[i,j])l[i,j] <- mu1*x[i,j]+ (1-x[i,j])*mu2[i,j]log(mu2[i,j])<- cov[i,j]*beta2 + alpha[i,j]alpha[i,j]~dnorm(0, tau_alpha)x[i,j] ~ dbin(p,1)

#These statements are for the benefit of GeoBugsmapx[j + (i-1)*N] <- x[i,j]mapy[j + (i-1)*N] <- y[i,j]mapl[j+(i-1)*N] <-l[i,j]

}}

}

Random effect

Page 25: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

NOTE: Possible mappings for the Scottish lip cancer data include

b – area-specific random effects term

mu – area-specific means

RR – area-specific relative risks

O – observed values

E – expected values

GeoBUGS Example

Page 26: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

The Scottish lip cancer example

Open a window in WinBUGS and insert the following items:- model

- data

- initial

values

#MODELmodel{for (i in 1 : N) { O[i] ~ dpois(mu[i]) log(mu[i]) <- log(E[i]) + alpha0 + alpha1 * X[i]/10 + b[i]# Area-specific relative risk (for maps) RR[i] <- exp(alpha0 + alpha1 * X[i]/10 + b[i])}# CAR prior distribution for random effects: b[1:N] ~ car.normal(adj[], weights[], num[], tau)for(k in 1:sumNumNeigh) { weights[k] <- 1}# Other priors:alpha0 ~ dflat() alpha1 ~ dnorm(0.0, 1.0E-5)tau ~ dgamma(0.5, 0.0005) # prior on precisionsigma <- sqrt(1 / tau) # standard deviation}

Page 27: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

#DATA

list(N = 56, O = c( 9, 39, 11, 9, 15, 8, 26, 7, 6, 20, 13, 5, 3, 8, 17, 9, 2, 7, 9, 7, 16, 31, 11, 7, 19, 15, 7, 10, 16, 11, 5, 3, 7, 8, 11, 9, 11, 8, 6, 4, 10, 8, 2, 6, 19, 3, 2, 3, 28, 6, 1, 1, 1, 1, 0, 0), E = c( 1.4, 8.7, 3.0, 2.5, 4.3, 2.4, 8.1, 2.3, 2.0, 6.6, 4.4, 1.8, 1.1, 3.3, 7.8, 4.6, 1.1, 4.2, 5.5, 4.4, 10.5, 22.7, 8.8, 5.6, 15.5, 12.5, 6.0, 9.0, 14.4, 10.2, 4.8, 2.9, 7.0, 8.5, 12.3, 10.1, 12.7, 9.4, 7.2, 5.3, 18.8, 15.8, 4.3, 14.6, 50.7, 8.2, 5.6, 9.3, 88.7, 19.6, 3.4, 3.6, 5.7, 7.0, 4.2, 1.8), X = c(16, 16, 10, 24, 10, 24, 10, 7, 7, 16, 7, 16, 10, 24, 7, 16, 10, 7, 7, 10, 7, 16, 10, 7, 1, 1, 7, 7, 10, 10, 7, 24, 10, 7, 7, 0, 10, 1, 16, 0, 1, 16, 16, 0, 1, 7, 1, 1, 0, 1, 1, 0, 1, 1, 16, 10),

Page 28: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

num = c(3, 2, 1, 3, 3, 0, 5, 0, 5, 4, 0, 2, 3, 3, 2, 6, 6, 6, 5, 3, 3, 2, 4, 8, 3, 3, 4, 4, 11, 6, 7, 3, 4, 9, 4, 2, 4, 6, 3, 4, 5, 5, 4, 5, 4, 6, 6, 4, 9, 2, 4, 4, 4, 5, 6, 5), adj = c(19, 9, 5, 10, 7, 12, 28, 20, 18, 19, 12, 1, 17, 16, 13, 10, 2,

29, 23, 19, 17, 1, 22, 16, 7, 2,

5, 3, 19, 17, 7, 35, 32, 31, 29, 25, 29, 22, 21, 17, 10, 7, 29, 19, 16, 13, 9, 7, 56, 55, 33, 28, 20, 4, 17, 13, 9, 5, 1, 56, 18, 4, 50, 29, 16, 16, 10, 39, 34, 29, 9, 56, 55, 48, 47, 44, 31, 30, 27, 29, 26, 15,

43, 29, 25, 56, 32, 31, 24, 45, 33, 18, 4, 50, 43, 34, 26, 25, 23, 21, 17, 16, 15, 9, 55, 45, 44, 42, 38, 24, 47, 46, 35, 32, 27, 24, 14, 31, 27, 14, 55, 45, 28, 18, 54, 52, 51, 43, 42, 40, 39, 29, 23, 46, 37, 31, 14, 41, 37, 46, 41, 36, 35, 54, 51, 49, 44, 42, 30, 40, 34, 23, 52, 49, 39, 34, 53, 49, 46, 37, 36, 51, 43, 38, 34, 30, 42, 34, 29, 26, 49, 48, 38, 30, 24, 55, 33, 30, 28, 53, 47, 41, 37, 35, 31, 53, 49, 48, 46, 31, 24, 49, 47, 44, 24, 54, 53, 52, 48, 47, 44, 41, 40, 38, 29, 21, 54, 42, 38, 34, 54, 49, 40, 34, 49, 47, 46, 41, 52, 51, 49, 38, 34, 56, 45, 33, 30, 24, 18, 55, 27, 24, 20, 18), sumNumNeigh = 234)

Page 29: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

#INITIAL VALUES

list(tau = 1, alpha0 = 0, alpha1 = 0,

b=c(0,0,0,0,0,NA,0,NA,0,0,

NA,0,0,0,0,0,0,0,0,0,

0,0,0,0,0,0,0,0,0,0,

0,0,0,0,0,0,0,0,0,0,

0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0))

Page 30: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

GeoBUGS Execution Instructions

Step 1: open a new window in WinBUGS (this will be referred to as the user window)

Step 2: enter the model syntax, data, and initial values, using the WinBUGS format, in the user window

Step 3: select “Specification” in the “Model” pull down window

Step 4: highlight “model” in the user window, appearing at the beginning of the model syntax, and click once on the “check model” button in the “Specification Tool” window

NOTE: feedback from the program appears in the lower left-hand corner of the WinBUGS program window,

and should be monitored

Page 31: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Step 5: highlight “list” in the user window, appearing at the beginning of the data, and click once on the “load data” button in the “Specification Tool” window

Step 6: insert the number of chains to be run (the default number is 1) in the “Specification Tool” window

Step 7: click once on the “compile” button in the “Specification Tool” window

Step 8: highlight “list” in the user window, appearing at the beginning of the initial values, and click once on the “load inits” button in the “Specification Tool” window (one set is needed for each chain to be run; clicking the “gen inits” button can be dangerous for sound analysis)

Page 32: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Step 9: close the “Specification Tool” windowStep 10: select “Samples” in the “Inference” pull

down menuStep 11: in the “Sample Monitor Tool” window:

type in the name (as it appears in the model syntax) of the 1st parameter to be monitored, and click once on the “set” button; type in the name of the 2nd parameter to be monitored, and click once on the “set” button; …; type in the name of the pth parameter to be monitored, and click once on the “set” button

Step 12: close the “Sample Monitor Tool” window

Page 33: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Step 13: select “Update” in the “Model” pull down menu

Step 14: the default value in the “updates” box is 1000this value most likely needs to be substantially increased (say, to 50,000; once any desired changes are made, click once on the “updates” button

Step 15: once the number appearing in the “iteration” box equals the number in the “updates” box, close the “Update Tool” window

Step 16: select “Samples” in the “Inference” pull down menu

Step 17: click on the down arrow to the right of the “node” box, and select the parameter to be monitored

Page 34: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Step 18: click once of the “history” button to view the time-series plot for all iterations; click once on the “trace” plot to view the time-series plot for the last iterations; click once on the “auto cor” button to view the time-series correlogram (you may wish to enlarge the graphic in this window); click once on the “stats” button to view a parameter estimate’s statistics

Step 19: close the “Sample Monitor Tool” windowStep 20: select “Mapping Tool” from the “Map” pull down

menuStep 21: select the appropriate map from the list appearing

for the “Map” box when the down arrow to its right is clicked once (hint: your map that you imported from an Arc shapefile should appear here)

Step 22: type the name of the variable (exactly as it appears in the model syntax) to be mapped in the “variable” box, and click once on the “plot” box

Page 35: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Puerto Rico Binomial with Spatial Autocorrelation Example

#MODEL

model{for (i in 1 : N) { U[i] ~ dbin(p[i], T[i]) p[i] <- exp(alpha0 + b[i])/(1+exp(alpha0 + b[i]))}# CAR prior distribution for random effects: b[1:N] ~ car.normal(adj[], weights[], num[], tau)for(k in 1:sumNumNeigh) { weights[k] <- 1}# Other priors:alpha0 ~ dflat() tau ~ dgamma(0.5, 0.0005) # prior on precisionsigma <- sqrt(1 / tau) # standard deviation}

Page 36: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

#DATAlist(N = 76, U = c(42527, 11048, 46236, 35859, 21330, 25584, 3792, 32126, 32389, 18664, 41997, 2839, 11787, 95880, 37713, 27605, 21499, 29709, 17200, 14688, 23829, 178792, 24196, 14767, 50242, 23848, 28462, 34650, 434374, 35130, 38583, 17412, 63929, 94085, 75728, 23852, 36971, 59572, 23364, 37238, 40919, 11062, 42042, 64685, 27305, 23077, 25387, 91593, 18346, 22105, 27850, 224044, 40875, 139445, 30886, 42467, 185703, 30071, 43707, 16671, 14262, 40457, 29802, 16800, 35270, 33421, 39958, 10176, 20682, 40395, 21087, 99850, 35476, 36201, 16472, 58848), T = c(44444, 17318, 50531, 36452, 26261, 34415, 11061, 34485, 32537, 19817, 45409, 6449, 12741, 98434, 39697, 29965, 23753, 29709, 23844, 20152, 26719, 186475, 25450, 14767, 52362, 25935, 31113, 37105, 434374, 40997, 44204, 21665, 63929, 94085, 75728, 35336, 37910, 61929, 27913, 39246, 46384, 19143, 42042, 64685, 29032, 26493, 28348, 100131, 19117, 22322, 28909, 224044, 46911, 140502, 35244, 43335, 186076, 30071, 47370, 18004, 19811, 42753, 37597, 20002, 36867, 34017, 40712, 12367, 21888, 44301, 23072, 100053, 36743, 38925, 16614, 59035),

num = c(4, 3, 5, 3, 4, 4, 3, 3, 5, 5, 3, 4, 5, 5, 3, 3, 6, 4, 7, 6, 4, 5, 4, 6, 7, 3, 2, 4, 6, 2, 7, 6, 8, 7, 5, 6, 7, 5, 6, 5, 4, 4, 8, 5, 5, 7, 6, 5, 6, 7, 6, 7, 6, 3, 5, 3, 7, 6, 5, 6, 7, 4, 3, 6, 5, 3, 3, 5, 6, 4, 5, 4, 2, 3, 2, 3),

Page 37: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

adj = c(2, 7, 14, 25, 1, 14, 21, 5, 8, 23, 31, 34, 9, 10, 29, 3, 6, 33, 34, 5, 7, 25, 33, 1, 6, 25, 3, 10, 23, 4, 11, 24, 29, 32, 4, 8, 23, 29, 31, 9, 12, 24, 11, 16, 19, 24, 17, 18, 28, 37, 39, 1, 2, 21, 25, 36, 17, 20, 22, 12, 18, 19, 13, 15, 22, 28, 38, 48, 13, 16, 19, 39, 12, 16, 18, 24, 35, 39, 45, 15, 22, 26, 41, 42, 46, 2, 14, 30, 36, 15, 17, 20, 46, 48, 3, 8, 10, 31, 9, 11, 12, 19, 32, 35, 1, 6, 7, 14, 33, 36, 44, 20, 27, 41, 26, 41, 13, 17, 37, 38, 4, 9, 10, 31, 32, 43, 21, 36, 3, 10, 23, 29, 34, 40, 43, 9, 24, 29, 35, 43, 50, 5, 6, 25, 34, 44, 49, 53, 60, 3, 5, 31, 33, 40, 49, 59, 19, 24, 32, 45, 50, 14, 21, 25, 30, 44, 47, 13, 28, 38, 39, 51, 52, 61, 17, 28, 37, 48, 52, 13, 18, 19, 37, 45, 51, 31, 34, 43, 59, 64, 20, 26, 27, 42, 20, 41, 46, 54, 29, 31, 32, 40, 50, 56, 57, 64, 25, 33, 36, 47, 53, 19, 35, 39, 50, 51, 20, 22, 42, 48, 52, 54, 68, 36, 44, 53, 58, 62, 63, 17, 22, 38, 46, 52, 33, 34, 59, 60, 66, 67, 32, 35, 43, 45, 51, 55, 57, 37, 39, 45, 50, 55, 61, 37, 38, 46, 48, 61, 68, 69, 33, 44, 47, 58, 60, 65, 42, 46, 68, 50, 51, 57, 61, 71, 43, 57, 64, 43, 50, 55, 56, 64, 71, 74, 47, 53, 62, 63, 65, 72, 34, 40, 49, 64, 67, 33, 49, 53, 65, 66, 76, 37, 51, 52, 55, 69, 70, 71, 47, 58, 63, 72, 47, 58, 62, 40, 43, 56, 57, 59, 74, 53, 58, 60, 72, 76, 49, 60, 67, 49, 59, 66, 46, 52, 54, 69, 73, 52, 61, 68, 70, 73, 75, 61, 69, 71, 75, 55, 57, 61, 70, 74, 58, 62, 65, 76, 68, 69, 57, 64, 71, 69, 70, 60, 65, 72, 2, 7, 14, 25, 1, 14, 21, 5, 8, 23, 31, 34, 9, 10, 29, 3, 6, 33, 34, 5, 7, 25, 33, 1, 6, 25, 3, 10, 23, 4, 11, 24, 29, 32, 4, 8, 23, 29, 31, 9, 12, 24, 11, 16, 19, 24, 17, 18, 28, 37, 39, 1, 2, 21, 25, 36, 17, 20, 22, 12, 18, 19, 13, 15, 22, 28, 38, 48, 13, 16, 19, 39, 12, 16, 18, 24, 35, 39, 45, 15, 22, 26, 41, 42, 46, 2, 14, 30, 36, 15, 17, 20, 46, 48, 3, 8, 10, 31,

9, 11, 12, 19, 32, 35, 1, 6, 7, 14, 33, 36, 44, 20, 27, 41, 26, 41, 13, 17, 37, 38, 4, 9, 10, 31, 32, 43, 21, 36, 3, 10, 23, 29, 34, 40, 43, 9, 24, 29, 35, 43, 50, 5, 6, 25, 34, 44, 49, 53, 60, 3, 5, 31, 33, 40, 49, 59, 19, 24, 32, 45, 50, 14, 21, 25, 30, 44, 47, 13, 28, 38, 39, 51, 52, 61, 17, 28, 37, 48, 52, 13, 18, 19, 37, 45, 51, 31, 34, 43, 59, 64, 20, 26, 27, 42, 20, 41, 46, 54, 29, 31, 32, 40, 50, 56, 57, 64, 25, 33, 36, 47, 53, 19, 35, 39, 50, 51, 20, 22, 42, 48, 52, 54, 68, 36, 44, 53, 58, 62, 63, 17, 22, 38, 46, 52, 33, 34, 59, 60, 66, 67, 32, 35, 43, 45, 51, 55, 57, 37, 39, 45, 50, 55, 61, 37, 38, 46, 48, 61, 68, 69, 33, 44, 47, 58, 60, 65, 42, 46, 68, 50, 51, 57, 61, 71, 43, 57, 64, 43, 50, 55, 56, 64, 71, 74, 47, 53, 62, 63, 65, 72, 34, 40, 49, 64, 67, 33, 49, 53, 65, 66, 76, 37, 51, 52, 55, 69, 70, 71, 47, 58, 63, 72, 47, 58, 62, 40, 43, 56, 57, 59, 74, 53, 58, 60, 72, 76, 49, 60, 67, 49, 59, 66, 46, 52, 54, 69, 73, 52, 61, 68, 70, 73, 75, 61, 69, 71, 75, 55, 57, 61, 70, 74, 58, 62, 65, 76, 68, 69, 57, 64, 71, 69, 70,

60, 65, 72), sumNumNeigh = 366)

#INITIAL VALUESlist(tau = 1, alpha0 = 0, b=c(0,0,0,0,0,0,0,0,0,0, 0,0,0,0,0,0,0,0,0,0, 0,0,0,0,0,0,0,0,0,0, 0,0,0,0,0,0,0,0,0,0, 0,0,0,0,0,0,0,0,0,0, 0,0,0,0,0,0,0,0,0,0, 0,0,0,0,0,0,0,0,0,0, 0,0,0,0,0,0))

queen’sconnectivity

definition

Page 38: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Model {

for (i in 1:N) {m[i] <- 1/num[i]}

cumsum[1] <- 0

for(i in 2:(N+1)) {cumsum[i] <- sum(num[1:(i-1)])}

for(k in 1 : sumNumNeigh)

{for(i in 1:N){pick[k,i] <- step(k - cumsum[i] - epsilon)*step(cumsum[i+1] - k)

# pick[k,i] = 1 if cumsum[i] < k <= cumsum[i=1];

otherwise, pick[k,i] = 0}

C[k] <- sqrt(num[adj[k]]/inprod(num[], pick[k,])) # weight for each pair of neighbours}

epsilon <- 0.0001

for (i in 1 : N) {

U[i] ~ dbin(p[i], T[i])

p[i] <- exp(S[i])/(1+exp(S[i]))

theta[i] <- alpha}

# proper CAR prior distribution for random effects:

S[1:N] ~ car.proper(theta[],C[],adj[],num[],m[],prec,rho)

for(k in 1:sumNumNeigh) {weights[k] <- 1}

# Other priors:

alpha ~ dnorm(0,0.0001)

prec ~ dgamma(0.5,0.0005) # prior on precision

sigma <- sqrt(1/prec) # standard deviation

rho.min <- min.bound(C[],adj[],num[],m[])

rho.max <- max.bound(C[],adj[],num[],m[])

rho ~ dunif(rho.min,rho.max)

}

Page 39: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

node mean sd MC error2.5% median 97.5% start samplerhoCAR 0.9378 0.05255 5.995E-4 0.8047 0.9514 0.9973 50001 10000

MCMC iteration correlogram

MCMC iteration time series plot

Page 40: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

GeoBUGS demonstration: % urban population in Puerto Rico – no

random effect#MODELmodel{for (i in 1 : N) { U[i] ~ dbin(p[i], T[i]) p[i] <- exp(alpha)/(1+exp(alpha ))}

# priors:alpha ~ dflat()}

Page 41: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

#DATAlist(N = 73, U = c(11062, 42042, 64685, 27305, 23077, 25387, 91593, 18346, 32281,

27850, 254115, 40875, 139445, 30886, 185703, 43707, 16671, 14262, 40457, 29802, 16800, 35270, 33421, 39958, 20682, 40395, 21087, 99850, 35476, 36201, 16472, 58848, 42527, 11048, 46236, 35859, 21330, 25584, 3792, 32126, 74856, 18664, 41997, 2839, 11787, 95880, 37713, 27605, 21499, 29709, 17200, 14688, 23829, 178792, 24196, 14767, 50242, 23848, 28462, 34650, 434374, 35130, 38583, 17412, 63929, 94085, 75728, 23852, 36971, 59572, 23364, 37238, 40919

), T = c(19143, 42042, 64685, 29032, 26493, 28348, 100131, 19117, 34689,

28909, 254115, 46911, 140502, 35244, 186076, 47370, 18004, 19811, 42753, 37597, 20002, 36867, 34017, 40712, 21888, 44301, 23072, 100053, 36743, 38925, 16614, 59035, 44444, 17318, 50531, 36452, 26261, 34415, 11061, 34485, 75872, 19817, 45409, 6449, 12741, 98434, 39697, 29965, 23753, 29709, 23844, 20152, 26719, 186475, 25450, 14767, 52362, 25935, 31113, 37105, 434374, 40997, 44204, 21665, 63929, 94085, 75728, 35336, 37910, 61929, 27913, 39246, 46384

),)#INITIAL VALUESlist(alpha=-3)

Page 42: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

The German labor market revisited:

frequentist and Bayesian

random effects models

Page 43: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Frequentist random intercept term

measure No covariates

Spatial filter

exponential semivariogram

-2log(L) 1445.1 1179.3 1349.8

Intercept variance

0.9631 0.2538 0.5873

Residual variance

0.6116 0.6011 0.9154

Intercept estimate

5.2827

(0.0599)

5.2827

(0.0443)

5.0076

(0.1835)

The spatial filter contains 27 (of 98) eigenvectors, with R2 = 0.4542, P(S-Wresiduals) < 0.0001.

Page 44: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

theproperCAR

model

MCMC results from GeoBUGS1000 weeded

25,000burn-in

Page 45: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Bayesian model estimation

measure No covariates

Spatial filter

CAR

-2log(L): post mean 1477.8 1213.4

Spatial structure parameter

*** 1.028

(0.0517)

Residual variance

1.69 0.9277

Intercept estimate

5.255

(0.0640)

5.258

(0.0473)

computerexecution

timerequired

toestimate

isprohibitive

Page 46: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

The ICAR alternative• #MODEL• model• {for (i in 1 : N) { • W[i] ~ dpois(mu[i])• log(mu[i]) <- alpha + S[i] + U[i] + log(A[i])

• U[i] ~ dnorm(0,tau.U) }

• # improper CAR prior distribution for random effects: • S[1:N] ~ car.normal(adj[],weights[],num[],tau.S)• for(k in 1:sumNumNeigh) {weights[k] <- 1}

• # Other priors:• alpha ~ dflat()• tau.S ~ dgamma(0.5, 0.0005) • sigma2.S <- 1/tau.S• tau.U ~ dgamma(0.5, 0.0005) • sigma2.U <- 1/tau.U }

offset

Page 47: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

• #DATA• list(N = 439, • W = c(• 25335, 74162, 64273, 25080, 39848, 59407, 49685, 60880, 101563, 39206, 83512, • … • 32999, 26534, 45267, 35232, 35788, 41961, 36129• ), • A = c(• 23.51, 43.81, 87.14, 27.53, 558.57, 512.17, 855.22, 578.86, 261.45, 447.18, 877.26, • …• 369.50, 382.46, 452.02, 350.84, 219.97• ), • num = c(1, 2, 4, 3, 4, 7, 2, 4, 4, 5, • …• 8, 7, 8, 4, 7, 7, 6, 8, 6• ),• adj = c(• 12, • 11, 10, • 359, 15, 8, 6, • … • 438, 400, 390, 375, 372, 368• ),• sumNumNeigh = 2314)

attributevariables

number of neighbors

lists of neighbors

This can begenerated by

GeoBUGS; thequeen’s definition

of adjacency is used

Page 48: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

• #INITIAL VALUES• list(tau.U=1, tau.S=1, alpha=0, • S=c(0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,

0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,• …•

0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0),

• U=c(0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,

• …•

0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0)

• )

Page 49: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

intercept

Convergence has not been achieved (10,000 burn in; + 25,000/100)

Page 50: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Random effects: spatially structured and unstructured

SA:2.67/(30.39+2.67)= 0.08(8% of variance)

Page 51: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Variance diagnostics

Page 52: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

bugs.R: functions for running WinBUGS from R

The bugs() function takes data and starting values as input, calls a Bugs model, summarizes inferences and convergence in a table and graph, and saves the simulations in arrays for easy access in R.

1st: Download WinBugs1.4 2nd: Download OpenBUGS and extract

the zip file into "c:/Program Files/“3rd: Go into R and type

install.packages("R2WinBUGS")

Page 53: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical

Some prediction comparisons

n = 56;

effective sample size = 24

Page 54: Lecture #4: Bayesian analysis of mapped data Spatial statistics in practice Center for Tropical Ecology and Biodiversity, Tunghai University & Fushan Botanical