This session covers exploratory tools and formal model-fitting procedures for investigating intensity.
The dataset japanesepines
contains the locations of Japanese Black
Pine trees in a study region.
Plot the japanesepines
data.
What is the average intensity (the average number of points per unit area?
Using density.ppp
, compute a kernel estimate of the
spatially-varying intensity function for the Japanese pines data,
using a Gaussian kernel with standard deviation
units, and store the estimated intensity in an object
D
say.
Plot a colour image of the kernel estimate D
.
Most plotting commands will accept the argument add=TRUE
and
interpret it to mean that the plot should be drawn over the existing
display, without clearing the screen beforehand. Use this to plot a
colour image of the kernel estimate D
with the original Japanese
Pines data superimposed.
Plot the kernel estimate without the ‘colour ribbon’.
Try the following command
persp(D, theta=70, phi=25, shade=0.4)
and find the documentation for the arguments theta
, phi
and
shade
.
Find the maximum and minimum values of the intensity estimate over
the study region. (Hint: Use summary
or range
)
The kernel estimate of intensity is defined so that its integral
over the entire study region is equal to the number of points in the
data pattern, ignoring edge effects. Check whether this is
approximately true in this example. (Hint: use integral
)
The bei
dataset gives the locations of trees in a survey area with
additional covariate information in a list bei.extra
.
Assign the elevation covariate to a variable elev
by typing
elev <- bei.extra$elev
Plot the trees on top of an image of the elevation covariate.
Assume that the intensity of trees is a function where is the terrain elevation at location u. Compute a nonparametric estimate of the function and plot it by
rh <- rhohat(bei, elev)
plot(rh)
Compute the predicted intensity based on this estimate of .
Compute a non-parametric estimate of intensity by kernel smoothing, and compare with the predicted intensity above.
Bonus info: To plot the two intensity estimates next to each other
you collect the estimates as a spatial object list (solist
) and
plot the result (the estimates are called pred
and ker
below):
l <- solist(pred, ker)
plot(l, equal.ribbon = TRUE, main = "",
main.panel = c("rhohat prediction", "kernel smoothing"))
The command rpoispp(100)
generates realisations of the Poisson process
with intensity in the unit square.
Repeat the command plot(rpoispp(100))
several times to build your
intuition about the appearance of a completely random pattern of
points.
Try the same thing with intensity .
Returning to the Japanese Pines data,
Fit the uniform Poisson point process model to the Japanese Pines data
ppm(japanesepines~1)
Read off the fitted intensity. Check that this is the correct value of the maximum likelihood estimate of the intensity.
The japanesepines
dataset is believed to exhibit spatial
inhomogeneity.
Plot a kernel smoothed intensity estimate.
Fit the Poisson point process models with loglinear intensity (trend
formula ~x+y
) and log-quadratic intensity (trend formula
~polynom(x,y,2)
) to the Japanese Pines data.
extract the fitted coefficients for these models using coef
.
Plot the fitted model intensity (using plot(fit)
)
perform the Likelihood Ratio Test for the null hypothesis of a
loglinear intensity against the alternative of a log-quadratic
intensity, using anova
.
Generate 10 simulated realisations of the fitted log-quadratic
model, and plot them, using plot(simulate(fit, nsim=10))
where
fit
is the fitted model.
The update
command can be used to re-fit a point process model using a
different model formula.
Type the following commands and interpret the results:
fit0 <- ppm(japanesepines ~ 1)
fit1 <- update(fit0, . ~ x)
fit1
fit2 <- update(fit1, . ~ . + y)
fit2
Now type step(fit2)
and interpret the results.
The bei
dataset gives the locations of trees in a survey area with
additional covariate information in a list bei.extra
.
Fit a Poisson point process model to the data which assumes that the
intensity is a loglinear function of terrain slope and elevation
(hint: use data = bei.extra
in ppm
).
Read off the fitted coefficients and write down the fitted intensity function.
Plot the fitted intensity as a colour image.
extract the estimated variance-covariance matrix of the coefficient
estimates, using vcov
.
Compute and plot the standard error of the intensity estimate (see
help(predict.ppm)
).
Fit Poisson point process models to the Japanese Pines data, with the following trend formulas. Read off an expression for the fitted intensity function in each case.
Trend formula | Fitted intensity function |
---|---|
~1 |
|
~x |
|
~sin(x) |
|
~x+y |
|
~polynom(x,y,2) |
|
~factor(x < 0.4) |
Make image plots of the fitted intensities for the inhomogeneous models above.
The dataset hamster
is a multitype pattern representing the locations
of cells of two types, dividing and pyknotic.
plot the patterns of pyknotic and dividing cells separately;
plot kernel estimates of the intensity functions of pyknotic and dividing cells separately;
use relrisk
to perform cross-validated bandwidth selection and
computation of the relative intensity of pyknotic cells.
The dataset ants
is a multitype point pattern representing the
locations of nests of two species of ants.
plot the data.
Fit the model ppm(ants ~ marks)
and interpret the result. Compare
the result with summary(ants)
and explain the similarities.
Fit the model ppm(ants ~ marks + x)
and write down an expression
for the fitted intensity function.
Fit the model ppm(ants ~ marks * x)
and write down an expression
for the fitted intensity function.
Compute the fitted intensities of the three models fitted above
using predict
and plot the results.
Explain the difference between the models fitted by ppm(ants ~
marks + x)
and ppm(ants ~ marks * x)
.
The study region for the ants’ nests data ants
is divided into areas
of “scrub” and “field”. We want to fit a Poisson model with different
intensities in the field and scrub areas.
The coordinates of two points on the boundary line between field and
scrub are given in ants.extra$fieldscrub
. First construct a function
that determines which side of the line we are on:
fs <- function(x,y) {
ends <- ants.extra$fieldscrub
angle <- atan(diff(ends$y)/diff(ends$x))
normal <- angle + pi/2
project <- (x - ends$x[1]) * cos(normal) + (y - ends$y[1]) * sin(normal)
factor(ifelse(project > 0, "scrub", "field"))
}
Now fit the models:
ppm(ants ~ marks + side, data = list(side=fs))
ppm(ants ~ marks * side, data = list(side=fs))
and interpret the results.