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Forest Region |
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Terrestrial amphibians are a relatively unstudied component of forest ecosystems in the Interior of British Columbia. Their populations had never been systematically examined and reported in the Cariboo Forest Region prior to this study.
Rotting logs provide protection from predators and a source of prey, while maintaining a microclimate with more constant temperature and humidity, which are generally good attributes for amphibian habitat. Burrowing amphibians inhabit the forest floor down to the mineral soil and are affected by soil characteristics, such as pH and depth of the forest floor. Timber harvesting and other management activities, such as broadcast burning, can affect these attributes.
Canopy cover affects evapotranspiration rates and thus ground moisture levels, and may also moderate ground temperature fluctuations. Changes to vegetation composition may also alter habitat suitability in many ways.
Density studies of amphibians in the Pacific Northwest have shown wide ranges, with high amphibian populations in patches of suitable habitat. Douglas-fir forests may have up to 180 salamanders per hectare.
Amphibians play an important role in forest ecosystems as predators of invertebrates and as prey for small mammals, birds and snakes. As a first step in biodiversity management, forest resource managers must know as much as possible about species ranges and frequencies. In addition, understanding of the effects of harvesting on populations will help allow a rational analysis of its impacts.
| Species | Adult Habitat | Food Source |
|---|---|---|
| Long-toed salamander | Underground, crevices and forest floor litter | Worms and arthropods |
| Western toad | Ground surface | Worms and arthropods |
| Wood frog | Ground surface | Worms and arthropods |
| Pacific treefrog | Arboreal and ground surface | Crawling and flying insects |
Table 2 summarizes the study results. Salamanders were most common in
the SBS, while toads and wood frogs were most frequent in the IDF, indicating
that terrestrial amphibian distribution varies by BGC zone. Salamanders
were not found in the ICH and their numbers could not be correlated with
coarse woody debris volume in either the IDF or SBS. There seems to be
no preference by salamanders for either clearcuts or forests.
| Species | IDF | SBS | ICH |
|---|---|---|---|
| Long-toed salamander | More in CC (> 27/ha) than F (none found) | Highest population and more in F (> 85/ha) than CC (> 32/ha) | None found |
| Western toad | Highest population and more in CC (> 27/ha) than F (> 9/ha) | More in CC than F through pitfall traps (hundreds trapped). None found with time-constrained search. | More in CC (> 11/ha) than F (none found) |
| Wood frog | More in CC (> 68/ha) than F (> 9/ha) | More in CC (> 11/ha) than F (none found) | None found |
| Pacific treefrog | Sporadic and low frequency with pitfall traps; none found by time-constrained search. | ||
Western toads and wood frogs were more frequent in clearcuts than forests, which contradicts other studies in warmer areas.
The two survey methods showed differences in species counts, probably as a result of the effects of differences in species mobility. Time-constrained searches could be expected to undercount toads and frogs, two species that can easily move away from a search area. Pitfall traps would likely undercount salamanders, which are less mobile (except during breeding season) and thus have less chance of reaching a trap.
The study confirms there are significant populations of four species of terrestrial amphibians in the Cariboo Forest Region. It shows that although salamanders are rarely seen by the casual observer, they are abundant. The study also suggests that clearcuts do not intrinsically exclude amphibians, and has raised the possibility that under some circumstances clearcuts may even benefit some terrestrial amphibians.
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