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A
project funded by the Joint Fire
Science Program
Woodlands dominated by piñon
and juniper occupy over 30 million hecatares of the western United
States. Prior to European settlement of this region during the late
1800s; the expansion of the piñon-juniper range may have only
just begun, since it currently occupies less area then climate conditions
seem to allow. Where woodlands are currently established, the type-conversion
from shrubland to woodland continues as understory shrub, bunchgrass,
and herbaceous species are slowly forced out as the overstory cover
of woodland tree species closes in on them. This vegetation type-conversion
leads to decreased species diversity, loss of soil seedbanks,
decreased aquifer recharge, increased soil erosion, and increased
chance of high intensity crown fires.
The range expansion of piñon juniper was associated with increased
fire return intervals due partly to fire suppression and the reduction
of surface fuels caused by the introduction of livestock grazing by
European settlers. In an attempt to return stands to pre-settlement
conditions dominated by sagebrush steppe and lower fire return intervals,
and to improve livestock forage and wildlife habitat, land managers
have attempted to reintroduce fire and manipulate fuel conditions using
mechanical, chemical, seeding, and fire treatments.
Where woodlands are dense, fire does not propagate easily except
under extreme fire weather conditions which typically results in
intense crown fires that have undesirable effects on soils and plants.
Where woodlands are more open and still possess surface fuels, managers
can create low to moderate intensity surface
fires with sporadic torching of larger trees, but even in these conditions
fire can be hard to propagate. For these reasons, sites have often
been prepped before burning, typically by chaining landscapes to
uproot trees and provide opportunities for early successional forbs,
grasses, and shrubs to re-establish. However, chaining results in
removal of both pre- and post-settlement trees and creates significant
soil disturbance, which is not compatible with the management goals
of many land management agencies, especially the National Park Service.
As a result, mechanical thinning or chemical treatment of post-settlement
trees is becoming more common, since it creates uneven-aged woodland
stands that are more natural and provide better wildlife habitat,
and does not create significant soil disturbance. Minimizing soil
disturbance is especially important in areas where cultural resources
may otherwise be at risk. Follow-up seeding of grasses has also been
used to help establish plant cover to minimize soil erosion, and
to increase fine fuel loads that are necessary to help re-establish
a low intensity surface fire regime.
Although there is some literature on the ecology and management of
piñon-juniper woodlands,
very little is known about the combined effects of thinning, seeding,
and burning, and effects are likely variable across its extensive
range extending from the Columbia plateau and Great Basin desert
to the Colorado plateau in western North America. Possible differences
across this geographic range include the presence of different species
of piñon, juniper, and understory plant species, and differences
in the ratio of summer:winter rainfall.
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