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Do natural disturbance regimes  provide realistic guidelines for  managing  early-successional habitats  in New England forests? 
Major forest types in northern U.S. Lull (1968)
 
 
~ 1880
~ 1930 >50% of forest vertebrates utilize early-successional stands
 
Obligate users RELATIVE USE 0 1.0 10 20 30 40 50 60 70 80 90 100 AGE OF STAND 0.5
Golden-winged warbler USGS
FOREST CLEARING FARM ABANDONMENT FOREST MATURATION Relative abundance of early-successional habitats RETURN TO PRE-COLUMBIAN CONDITIONS ?
How much was there?
source: Harvard Forest
Methods to Estimate  Natural Disturbance Regimes   Lorimer and White (2003) ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Large-scale fires infrequent in New England, ~800-1,200 years  1790 survey in NY found that 1% of landscape burned or open.
Small-scale wind storms:  kill one to several trees.  In eastern U. S., 0.2- 2%/year of all forests are affected by wind throw.  At any time, 5-50% of a forest may be affected.
Large-scale wind storms:  hurricanes or tornadoes at irregular intervals (1635, 1788, 1815, 1938, and 1944). 1938 hurricane affected >240,000 ha  in New England Boose et al. (2001)
Approximate return interval of  damaging (F2) hurricanes in  New England. Boose et al. (2001) 85 yr 150 yr 380 yr >380 yr
 
Wilson 2005 Lumber Exports (Wilson 2005) vs Witness Trees Projections (Lorimer 1977): very different estimates of the prominence of white pine (>10x), indicating a large difference in the frequency and scale of disturbance in these forests.
Northern Hardwoods seedling/sapling (1-15 yrs):  1-3% young pole (15-30 yrs):  1-3%   2-6% Pitch Pine- Scrub Oak seedling/sapling: 10-30% young pole:  10-30%   20-60% (Lorimer and White 2003)
Trani et al. (2001) Early-successional forests in the eastern U.S. 9% 4%
What About Biotic Disturbances?
Contemporary Herbivores
flooded forest  pond  wet meadow  shrubs  forest
Open water areas created by beaver dams on the Kabetogama Peninsula, northern MN . 1940: 1% of area 1986: 13% of area Johnston and Naiman (1990) How large an area  affected?
Northern Hardwoods seedling/sapling  1-3% young pole    1-3% beaver flowages  ~ 3.5% (Gotie and Jenks 1982)   5-11% (Lorimer and White 2003)
Even if we can accurately estimate HRNV, are these values relevant  in contemporary landscapes?
40/mi 2 1100/mi 2 POPULATION DENSITY
Hoving (2001) Road Density in the Northeast
 
 
 
 
0 20 40 60 80 100 COMPOSITION (%) 0 20 40 60 80 100 120 140 RACCOON/CANID TRACKS CANIDS RACCOONS LANDSCAPE FOR DEV AGR
   2.5 ha    5 ha Winter mortality: Patches   69% 35%
OCT NOV DEC JAN FEB MAR APR MAY FOOD QUALITY LARGE PATCHES SMALL  PATCHES THRESHOLD? CONDITION-SENSITIVE PREDATION
9 JAN 16 JAN 23 JAN 30 JAN 6 FEB 13 FEB 20 FEB 27 FEB 6 MAR 13 MAR 20 MAR 27 MAR 3 APR 10 APR 0 2 4 6 8 10 12 UN:C  RATIO 4 3 3 3 4 5 6 3 2 5 13 11 13 13 12 6 2 9 7 7 8 5 5 5 8 5 4 4
New approaches needed to provide habitat
Parcelization or Fragmentation potential to mimic  natural disturbances restoration of shrublands/ modified disturbance regime (“sliding scale”) modified disturbances (large and clustered/connected) limited extreme Forest Age young old
MANAGING INDUCED METAPOPULATIONS: may require deviating from HRNV ME NH VT NY MA CT RI
 
 
 
DESCRIBING HABITAT  DISTURBANCES Size Frequency Intensity
 
Do natural disturbance regimes  provide realistic guidelines for  managing early-successional habitats  in New England forests? 
 
Human-generated disturbances
Pisgah Forest in southwestern New Hampshire three years after 1938 hurricane.

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