Keith B. Aubry
U.S. Forest Service
PNW Research Station
Twice each summer in all treatments, a foliated branch was clipped at 3 crown levels of 1 overstory
Douglas-fir, and near the ground on 3 understory vine maples. This was done for 1 year prior to treatment, and for 2 consecutive years after treatment.
Canopy arthropods showed little response to DEMO harvest treatments - changes in abundance in the harvest treatments were similar to those in the controls.
At the scale of this study, canopy arthropods responded more to regional variation in environmental conditions and changing weather patterns than to changes in canopy structure.
Litter arthropods more likely to respond to DEMO harvest treatments than canopy species.
Sensitivity to changes in moisture, temperature, and availability of resources.
Litter-dwelling spiders and carabid beetles
5–7 years after harvest, used small pitfall traps with preservative during summer for 2 years in
5 of the 6 treatments in 4 of the 6 blocks.
Xeric- or open-habitat spiders increased after timber harvest.
Interior-forest spiders decreased.
Level of retention had little effect on the magnitude of decreases.
Pattern of retention had no effect on responses by any group of spiders.
Abundance and species richness of carabid beetles declined significantly in the harvest treatments.
Open-habitat species did not colonize harvested units as expected.
As with spiders, level and pattern of retention had little effect on the magnitude of treatment responses.
Interior-forest spiders and carabid beetles declined significantly in abundance with proximity to forest edge.
Aggregates provided better habitat than clearcut areas for interior-forest species in both groups, but provided poorer habitat conditions than undisturbed forest.
5-7 years after harvest, none of the treatments provided suitable habitat for forest-dependent, litter-dwelling spiders or carabid beetles.
Strong edge-related declines in 1-ha aggregates suggest that smaller patches permitted under the NWFP (0.2-1.0 ha) are unlikely to support many old-forest taxa .
All wildlife sampling – 2 consecutive years both before and soon after harvests.
Amphibians & forest-floor small mammals
Pitfall trapping for 4 weeks after the onset of fall rains.
Breeding birds
Point-counts (all 6 blocks) and territory or spot-mapping (4 WA blocks only) during spring.
No evidence that salamanders responded to level or pattern of retention 2 years after harvest.
Due to their longevity and high sitetenacity, responses to harvest probably occur over longer time frames.
Captures after harvest were associated with ground cover (CWD or herbs).
Among interior-forest species, only the western red-backed vole responded negatively to harvest intensity.
Others – neutral or inconsistent reponses.
Open-habitat species (deer mouse, longtailed vole, and creeping vole) generally increased with harvest intensity.
No responses to pattern of retention.
Responses strongly influenced by regional variation in habitat conditions and species composition.
Western red-backed voles were significantly reduced or extirpated in all harvested areas – persisted only in undisturbed forest or in the aggregates.
Abundance lower in aggregates than controls
– lower habitat value than undisturbed forests.
2 years after harvest, canopy-nesting and bark-gleaning birds responded negatively to 15% retention, regardless of pattern.
Golden-crowned
Kinglet 7
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Creeper
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Negative responses to 15% retention also seen in reproductive indices.
Chestnut-backed
Chickadee
In the short term, intensity of post-harvest treatments may have a greater effect on responses of salamanders and small mammals than level or pattern of retention.
Providing CWD volume and herb cover in managed forests would improve habitat quality.
For many small mammals, regional differences in moisture regimes will influence the amount of retention needed to obtain comparable habitat benefits.
Except for western red-backed voles, which persisted only in aggregated retention, the pattern of retention had little effect on forest-floor arthropods, amphibians, small mammals, or birds at the treatment level.
Although aggregates are “lifeboats” for many forest attributes over the short term, for many interior-forest arthropods and mammals, aggregates >1 ha will be needed.
Retention levels at or below 15% appear to be inadequate to maintain populations of canopy-nesting or bark-gleaning birds over the short term.
For this and all other response variables, continued research is needed to determine how responses change as the
DEMO stands develop.
This past year, a team of 4 PNW scientists conducted a comprehensive re-assessment of the wildlife component of DEMO.
What worked? What didn’t? Why not?
Information obtained from that assessment, this workshop, and other sources will be used to improve the quality of future wildlife research in DEMO.
Similar process for other disciplines.