Figure 4

Figure 5

|
METHODS
I gathered spatial datasets from provincial and
federal sources to build a Geographic Information System (GIS) for the study
area using ArcGIS v 9.3.0.1770
(Table 1).
|
Dataset
|
Source
|
Notes
|
|
Vegetation Resource Inventory (VRI)
|
Ministry of Forests and Range, British Columbia (Geographic
Data Discovery Service 2009)
|
A vector layer derived through interpretation of
aerial imagery to assign attributes, such as age projections, species
compositions, and disturbance histories to discrete patches of forest
vegetation, termed “polygons”.
|
|
Digital Elevation Model (DEM)
|
Ministry of Natural Resources, Canada (Canadian
Digital Elevation Data 2009)
|
To align the DEM to the VRI, I converted the DEM to a
raster with cell size of 25 m by 25 m before reprojecting using bilinear
sampling.
|
|
Roads
|
Natural Resources Canada (Natural
Resources Canada 2009)
|
A vector layer of road centre lines derived from
multiple sources including GPS and verified through orthophotos.
|
|
HNFR
|
Blackwell et al. 2003
|
A vector layer that estimates boundaries in
Historic Natural Fire Regime according to aspect, elevation, slope, and
dominant vegetation.
|
Table 1. Datasets Built in GIS for Analyses.
Since
my questions focus on the historic role of fire, I removed polygons from the
vegetation layer that did not support fire according to the layer of HNFR.
These polygons fell into two categories:
1. water bodies and
2. rocky areas located in alpine
areas (Figure 4).
I performed all subsequent analyses on polygons that
contained vegetation and support fire. First,
I subdivide the vegetated polygons that support fire into two groups according
to projected age to reflect stands that likely established prior to European settlement (1860):
1. ≥ 200 years old (old) and
2. < 200 years old (young)
.
For
all polygons within each category, I assigned a point to each polygon centre to
calculate slope, aspect, elevation, and solar radiation by extracting values
from my DEM to the points that represented each polygons. I computed a distance
from nearest road from each point using the Euclidean Distance tool using the roads
layer. Since
observations from the field indicated a direct relation between age and
elevation, I plotted these variables against each other on a scatter plot to inspect the variance of age with elevation (Figure 5).
I used a chi-squared test to test for independence between age
and elevation. Then I built a model to predict stand age using elevation,
aspect, solar radiation and distance from nearest road. In this model stand age
is a the dependent response variable and each stand is binomially distributed,
where stands ≥ 200 years old are assigned a value of 1 and all other stands are
assigned a value of 0. The logistic regression model predicts stand for all
stands to parameterize a probability curve of age:

where Pr is the probability that
stands are ≥ 200 years old and Mx is the model of the likelihood of
old stands that contains the independent variable(s). In the simplest case, the
model of stand age (M1) includes only one independent variable:
 Where
t is time since fire in years, and α
and β are calculated coefficients for the regression. I incorporated
topographic variables along with distance from road into the model in a forward
step-wise process to determine influences on stand age. I used Akaike's information criterion (AIC), a tool for model selection that
assesses goodness of fit between model by measuring the relative amount of information
lost in a given model, to select the best model. AIC value is calculated with
the following formula:
AIC
= -2(maximized log-likelihood) + 2K
where
K is the number of
parameters and the maximized
log-likelihood is the natural logarithm of the likelihood function
for a particular model. All subsequent analyses were performed using
Statistical Analysis System (SAS) v9.1 (SAS Institute, Cary, NC, USA). All
tests were significant using alpha = 0.05.
|
| |