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Post-Wildfire Logging Hinders Regeneration and Increases Fire Risk
D. C. Donato,1* J. B. Fontaine,2 J. L. Campbell,1 W. D. Robinson,2 J. B. Kauffman,3 B. E. Law1
1Department of Forest Science, Oregon State University, Corvallis, OR 97331, USA. 2Department of Fisheries and Wildlife,
Oregon State University, Corvallis, OR 97331, USA. 3Institute of Pacific Islands Forestry, USDA Forest Service, Pacific
Southwest Research Station, 60 Nowelo Street, Hilo, HI 96720, USA.
*To whom correspondence should be addressed. E-mail: dan.donato@oregonstate.edu
Recent increases in wildfire activity in the United States have
intensified controversies surrounding the management of
public forests after large fires (1). The view that postfire
(salvage) logging diminishes fire risk via fuel reduction, and
that forests will not adequately regenerate without
intervention that includes logging and planting, is widely held
and commonly cited (2, 3). An alternative view maintains that
postfire logging is detrimental to long-term forest
development, wildlife habitat and other ecosystem functions
(1). Scientific data directly informing this debate are lacking.
Here we present data from a study of early conifer
regeneration and fuel loads following the 2002 Biscuit Fire,
Oregon, USA, with and without postfire logging. Because of
the fire's size (~200,000 hectares), historic reforestation
difficulties in the region (4), and an ambitious postfire
logging proposal, the Biscuit Fire has become a national icon
of postfire management issues. We used a spatially nested
design of logged and unlogged plots replicated across the fire
area and sampled before (2004) and after (2005) logging (5).
Natural conifer regeneration on sites that experienced
high-severity fire was variable but generally abundant, with a
median stocking density of 767 seedlings per hectare,
primarily of Douglas-fir (Pseudotsuga menziesii) (Fig. 1A).
Such density exceeds regional standards for fully stocked
sites, suggesting that active reforestation efforts may be
unnecessary. Postfire logging subsequently reduced
regeneration by 71%, to 224 seedlings per hectare (Fig. 1A),
due to soil disturbance and physical burial by woody material
during logging operations. Thus, if postfire logging is
conducted in part to facilitate reforestation, replanting could
result in no net gain in early conifer establishment.
Postfire logging significantly increased both fine and
coarse downed woody fuel loads (Fig. 1B). This pulse was
comprised of unmerchantable material (e.g., branches), and
far exceeded expectations for postfire logging-generated fuel
loads (5, 6). In terms of short-term fire risk, a reburn in
logged stands would likely exhibit elevated rates of fire
spread, fireline intensity and soil heating impacts (7).
Postfire logging alone was notably incongruent with fuel
reduction goals. Fuel reduction treatments (prescribed
burning or mechanical removal) are frequently intended
following postfire logging, including in the Biscuit plan, but
resources are often not allocated to complete them (8). Our
study underscores that, after logging, mitigation of short-term
fire risk is not possible without subsequent fuel reduction
treatments. However, implementing these treatments is also
problematic. Mechanical removal is generally precluded by
its expense, leaving prescribed burning as the most feasible
method. This will result in additional seedling mortality and
potentially severe soil impacts due to long duration
combustion of logging-generated fuel loads. Therefore, the
lowest fire risk strategy may be to leave dead trees standing
as long as possible (where they are less available to surface
flames), allowing for aerial decay and slow, episodic input to
surface fuel loads over decades.
Our data show that postfire logging, by removing naturally
seeded conifers and increasing surface fuel loads, can be
counterproductive to goals of forest regeneration and fuel
reduction. In addition, forest regeneration is not necessarily in
crisis across all burned forest landscapes. The results
presented here suggest that postfire logging may conflict with
ecosystem recovery goals.
References and Notes
1. D. B. Lindenmayer et al., Science 303, 1303 (2004).
2. U.S. House Committee on Resources, Forest Recovery Bill
Hearing Press Release (November 9, 2005).
3. J. Sessions, P. Bettinger, R. Buckman, M. Newton, J.
Hamann, J. For. 102, 38 (2004).
4. S. D. Tesch, S. D. Hobbs, W. J. Appl. For. 4, 89 (1989).
5. Materials and methods are available as supporting material
on Science Online.
6. Timber decay associated with delays in postfire logging
was anticipated to exacerbate the observed pulse of surface
fuel. However, our data indicate that delay was responsible
for ~10% of woody fuel present after logging.
/ www.sciencexpress.org / 5 January 2006 / Page 1 / 10.1126/science.1122855
7. J. K. Agee, Fire Ecology of Pacific Northwest Forests
(Island Press, Washington, DC, 1993).
8. R. W. Gorte, “Forest Fires and Forest Health”
Congressional Research Service (Publication 95-511,
1996).
9. This work was supported by the Joint Fire Science
Program and DOE grant DE-FG02-04ER63917. We thank
field technicians and the Siskiyou National Forest.
Supporting Online Material
www.sciencemag.org/cgi/content/full/1122855/DC1
Materials and Methods
SOM text
References and Notes
21 November 2005; accepted 21 December 2005
Published online 5 January 2006; 10.1126/science.1122855
Include this information when citing this paper.
Fig. 1. Natural conifer regeneration (A) and surface woody
fuel loads (B) before and after postfire logging of the Biscuit
Fire, Oregon, USA. (A) Regeneration was abundant
following fire. Postfire logging significantly reduced seedling
densities (P<0.01, Wilcoxon signed rank test) from 767
seedlings ha1 to 224 seedlings ha1. (B) Postfire logging
significantly increased downed fine (P<0.01) and coarse
(P<0.05) woody fuel loads (Mg ha-1) relative to burn-only by
Wilcoxon signed rank test. To provide context, fuel data from
unburned stands are shown as reference for pre-fire
conditions (fuel loads in burn-logged stands were at or well
above pre-fire levels). Graphs of seedling densities and fine
(<7.62) and coarse (>7.62) surface woody fuels are medians +
SE; n = 8 stands for no burn, n = 9 for burn-only and burnlogged
(5).
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