Prescribed
Burning in Shrublands
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Montaña
de Oro is a California State Park located not far from the Cal Poly
Campus. This park is typical of many, in that it contains plant communities
adapted to fire, but it is also adjacent to developed areas where people
live. Prescribed burning in the park is therefore a difficult and potentially
dangerous undertaking. Some plant species in Montaña de Oro are
actually dependent on fire for regeneration, similar to many found in
California's shrublands. One such shrub, known as "Morro
manzanita" (Arctostaphylos morroensis), is an endangered
species and found only in the immediate vacinity of Montaña de
Oro.
To gain a better understanding
of how fire should be used in the management of Morro manzanita, a prescribed
burn was performed in a small portion of the plant's current distribution.
Claudia
Tyler (Institute for Computational Earth Systems Science, UCSB) and
Dennis Odion (Marine Science
Institute, UCSB) were the PI's on this project. I participated in the
pre- and post-burn sampling, as well as monitoring during the fire. Our
main goal was to determine which factors prior to the fire (e.g., species
composition and fuel loading) and during the fire (e.g., fire intensity
and fuel consumption) relate most strongly to successful regeneration.
Click here to see the approximate location
of this fire, which was ~10 acres in size.
Almost none of the
Morro manzanita shrubs survived in areas that actually burned. Regeneration
of Morro manzanita has also been extremely low, far below that needed
for long-term persistence of this species. The possible causes for the
lack of regeneration (e.g., low fire intensity and/or not enough time
since the last fire to build up sufficient seedbank) are still under consideration.
However, one of the clear lessons of this project is that successful prescribed
burning may be more complex than we assume for plant species that are
adapted to fire at relatively specific fire intervals or intensities.
Prescribed fires can result in local extirpation of important native species,
even when their persistence is the main management goal. Follow this link
to the abstract of the report for this project.
Some related photos are included below.
On the day of this fire (November 4, 1998), winds
were light and onshore, making for relatively cool and humid conditions.
It had also rained 10 days earlier, so soil moistures were relatively
high. Once ignited, the fire proceeded through the study area at
a slow and variable rate.
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In many prescribed fires, a road or some other feature
on the landscape is useful for keeping the fire in check. Here
we see fire-fighting personel monitoring the perimeter for "spotting,"
or spreading to start new fires via airborn embers.
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The fire generally stopped spreading where fuel
was not continuous. However, flame lengths were in excess of 50
ft in some of the thicker stands of brush (note the height of
the person in lower right of this figure).
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In much of the study area, the fire consumed mostly
fine fuels (leaves, twigs, and litter). As a surrogate measure
for fire intensity, we set out cans with a pre-measured amount
of water in them. Cans were later retrieved, and the amount of
water boiled off was recorded.
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Mortality of the few A. morroensis seedlings
that did emerge was very high, and much of the ground is still bare.
Most of the post-burn vegetation consists of resprouts or adults
of other species that survived the fire, and some areas are dominated
by invasive veldt grass (Ehrharta calycina).
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Last updated: <February, 2003>
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