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specifically designed to estimate canopy fuel characteristics, computes both
CBH
and
CH
by multiplying the maximum
CBD
by 0.1 up to the
CBD
threshold of
0.012 kg m
−3
. Since
CBH
and
CH
can be computed from so many diverse methods,
it is important that those who use canopy fuel data to simulate fire behavior know
how
CBH
and
CH
were calculated.
There are many aspects of the two canopy height estimates that may compro-
mise their use in fire behavior analyses. First, regardless of what method is used to
estimate
CBH
and
CH
from the modeled
CBD
canopy profile, the resolution of that
estimate is governed by the width of the horizontal canopy layer used to summarize
CBH
vertical distribution. This is somewhat of a double-edged sword in that thin
layer widths (high resolution) rarely match the resolution of the tree input data used
to calculate the
CBD
estimates, but, the thicker layer widths that better match the
scale of the data (> 1 m) may be too coarse to recognize subtle differences created
by fuel treatments. Input tree data often contain only heights of the tree and crown
base, and rarely have finer crown measurement resolutions. Second, surface fuels
may have more importance in crown fire initiation than low
CBH
values. A small
fire can ignite a canopy if there are sufficient ladder fuels at a tree-level, and a large
fire can ignite a canopy no matter the
CBH
. And lastly and most importantly, the
scale of
CBH
and
CH
measurements do not match the scale of the point-scale simu-
lation models that simulate these processes, similar to
CBD
. The coarse resolutions
of point-level, crown fire simulation in most fire behavior prediction systems is
often incompatible with the fine-scale spatial distribution of
CBH
and
CH,
and the
fine scales at which fire spreads. As a result, one can view
CBH
and
CH
as indices
rather than actual measurements, and it is often a common practice to adjust the
calculated or measured values to values that represent more realistic fire behavior.
4.3.4
Canopy Fuel Load
CFL (kg m
−2
) is used to estimate the amount of canopy material consumed in a
crown fire (
CFB
in Eq. 4.7), and it is defined as the amount of burnable canopy fuel
per unit area.
CFL
is also quite useful in fire effects simulations, such as the esti-
mation of smoke emissions (Ward
1995
), because it provides a somewhat accurate
representation of actual biomass consumed in a crown fire.
CFL
isn't really related to any of the other three canopy characteristics
(Table
4.1
). While an estimate of
CFL
could be made by multiplying
CBD
by the
difference between
CH
and
CBH,
this would assume an even distribution of
CBH
across the canopy fuel profile similar to van Wagner (
1977
) assumptions, but this is
rarely observed as is evidenced by the profiles in Fig.
4.3
only a few methods cal-
culate
CBD
as an average across the canopy profile (Cruz et al.
2003
). FuelCalc, for
example, estimates
CBD
as a maximum running average (Reinhardt et al.
2006a
).
Therefore,
CFL
needs to be estimated and mapped directly to ensure accurate and
consistent fire applications.
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