Bark beetle infestations are an interesting emergent
complication in forest management in a changing climate. As temperature and
precipitation patterns change, we a seeing a subsequent shift in ranges of not
only plants, but animals as well. The trouble for [most] plants, is that they
are not able to physically move northward or upslope as their preferred weather
regime slips away year after year. Instead, long-lived plants must stay in
place and soldier on through droughts and heat waves which substantially stress
the plant and make it susceptible to pests and disease. Conversely, these
weather changes are good fortune for most insects through northerly expanded
ranges, less lethal winters, and landscapes of sickly trees for easy
pickings. After an unusually warm winter most insect populations expand, and
critters like bark beetles are no different, multiplying like crazy through a
protracted breeding period in new expanses where the vegetation have no
effective defenses. The result: acres upon acres of dead and dying trees.
Image by WikiSpaces |
Early
in the infestation, fine surface fuels may increase as the weakest and oldest
trees succumb to beetle predation. Fire during this stage might be low-intensity,
low-severity depending on the resilience of the associate vegetation. As the
infestation progresses, the proportion of shed limbs and snags increases,
increasing fuel continuity and the presence of ladder fuels. Fire at this point
has high-intensity potential because the incidence for crown fires increases
substantially. Late in the infestation most trees are dead and depending on how
many years it took the stand to succumb, a significant portion of these dead
trees could now litter the ground increasing both fuel continuity and fuel
density. Fire at the end stages of bark beetle infestation would have the
highest potential for severity as a surface fire as most of the aerial fuels
have likely been removed by this time.
Another consequence of beetle-kill is
the elimination of the patchy nature of most wildland fires. A landscape covered
with large, continuous fuels may not have any natural fire breaks and will probably
be stand-replacing. The regeneration following such a fire will be even-aged
and of a different composition than pre-infestation, since the productivity and
recruitment of the host species was handicapped for so long. Successive infestations
and fires may facilitate the extirpation of once-abundant species as ranges and
climate patterns continue to shift.
These pictures illustrate the potential of a high insistent fire. Just amazing that a beetle can devastate such large landscapes. I'm convinced that it is a combination of two impacts. And we could say the bark beetle increases fire just because it has successfully impacted vast stands of trees and like you note, this is not like a natural patchy wildfire. A tree that is drying out from temperature change and reduced water is an invitation to bark beetles. Weakened trees also allow for greater potential damage from the bark beetle. This increases the amount of dry dying fuel which increases fire.
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