Abstract
The mountain ecotype of the woodland caribou (Rangifer tarandus caribou) is highly dependent on the arboreal hair lichens Bryoria spp. and Alectoria sarmentosa during winter. In parts of British Columbia, partial-cutting silvicultural systems have been used in an effort to provide continuously usable winter habitat for mountain caribou, while allowing some timber removal. We reviewed available information about the changes in hair lichens after partial cutting in Engelmann spruce (Picea engelmannii) – subalpine fir (Abies lasiocarpa) forests of British Columbian and Idaho. Generally, abundance of Bryoria spp. in the lower canopy of individual residual trees increases with increased exposure after partial cutting, until the new regeneration begins to shelter the lower canopy of the residuals. Heavy basal area removal, however, results in low lichen availability at the stand level for many years. Abundance of Bryoria on the regeneration is low, and appears to be limited largely by the structure of the young trees, not by lichen dispersal, although dispersal capability may be limiting in Alectoria. Both distributional and physiological data suggest that Bryoria is intolerant of prolonged wetting, and that increased ventilation, rather than increased light, accounts for enhanced Bryoria abundance in the partial cuts. Alectoria sarmentosa reaches its physiological optimum in the lower canopy of unharvested stands; its growth rates are somewhat reduced in the more exposed environment of partial cuts. Both genera are capable of rapid growth: over a 7-year period, individual thalli of A. sarmentosa and Bryoria spp. (excluding those with a net biomass loss due to fragmentation) in an unlogged stand more than tripled their biomass. Calculated growth rates, as well as dispersal potential, are influenced by fragmentation. Bryoria produces more abundant, but smaller, fragments than Alectoria, and fragmentation in both genera increases in partial cuts. In subalpine mountain caribou habitat, partial-cutting prescriptions that enhance exposure of residual trees while keeping basal area removal low will maintain forage best. Regeneration management should focus on maintaining ventilation in the lower canopy of the residual stand.
Highlights
In British Columbia, Canada, the range of the mountain ecotype of the woodland caribou (Rangifer tarandus caribou) is closely associated with the Interior Wetbelt (Stevenson et al, 2001; Apps & McLellan, 2006), an area of high precipitation located on the western slopes of the Rocky Mountains
Even before they were formally considered to be at risk, the mountain caribou were a species of management concern because of their declining numbers and their apparent sensitivity to resource development and human activity within their range (Stevenson & Hatler, 1985)
Clearcut forest harvesting was thought to be incompatible with the conservation of mountain caribou, which were known to be closely associated with old-growth forests
Summary
In British Columbia, Canada, the range of the mountain ecotype of the woodland caribou (Rangifer tarandus caribou) is closely associated with the Interior Wetbelt (Stevenson et al, 2001; Apps & McLellan, 2006), an area of high precipitation located on the western slopes of the Rocky Mountains. The studies of hair lichen abundance in high-elevation mountain caribou range discussed in the previous sections revealed that Alectoria sarmentosa is often abundant in the lower canopy of old stands, and sparse or absent in the upper canopy. It remains present on residual trees after partial cutting, but does not exhibit a conspicuous increase in biomass. It is extremely sparse or absent on young regeneration after partial cutting These studies showed that Bryoria spp. are present throughout the canopy in old Engelmann spruce-subalpine fir stands, but reach their highest abundance in the mid to upper canopy.
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