EXECUTIVE SUMMARY
4/17/2000
Read the complete Final
Proposal (4/17/2000) as an MS Word document. (666kb)
Introduction
Many U.S. forests, especially those with historically short-interval,
low- to moderate-severity fire regimes, are too dense and have excessive
quantities of fuels. Widespread treatments are needed to restore
ecological integrity and reduce the high risk of destructive,
uncharacteristically severe fires in these forests. Among possible
treatments, however, the appropriate balance among cuttings, mechanical
fuel treatments, and prescribed fire is often unclear. For improved
decisionmaking, resource managers need much better information about the
consequences of alternative management practices involving fire and
mechanical/manual "fire surrogates."
Long-term, interdisciplinary research thus should be initiated to
quantify the consequences and tradeoffs of alternative fire and fire
surrogate treatments. Both ecological and economic aspects must be
included as integral components. The research needs to be experimental,
rather than retrospective or correlative, to permit stronger inferences
about cause-and-effect relationships. Only through such research will it
be possible to determine which ecosystem functions of fire can be
emulated satisfactorily by other means, which may be irreplaceable, and
the implications for management. The human dimensions of the problem are
also important. Treatment costs and utilization economics, as well as
social and political acceptability, strongly influence decisions about
treatment alternatives. Such research must be a cooperative effort,
involving land managers, researchers, and other interested parties.
A team of scientists and land managers has designed an integrated
national network of long-term research sites to address this need, with
support from the USDA/USDI Joint Fire Science Program (http://www.nifc.gov/joint_fire_sci/index.html).
The steering committee and other participants in this national
"Fire/Fire Surrogate" (FFS) study represent a number of
federal and state agencies, universities, and private entities, as well
as a wide range of disciplines and geographic regions. The study will
use a common experimental design to facilitate broad applicability of
results.
Objectives
Objectives of the project are as follows:
1. Quantify the initial effects (first five years) of fire and fire
surrogate treatments on a number of specific core response variables
within the general groupings of (a) vegetation, (b) fuel and fire
behavior, (c) soils and forest floor (including relation to local
hydrology), (d) wildlife, (e) entomology, (f) pathology, and (g)
treatment costs and utilization economics.
2. Provide an overall research design that (a) establishes and
maintains the study as an integrated national network of long-term
interdisciplinary research sites utilizing a common "core"
design to facilitate broad applicability of results, (b) allows each
site to be independent for purposes of statistical analysis and
modeling, as well as being a component of the national network, and
(c) provides flexibility for investigators and other participants
responsible for each research site to augment--without
compromising--the core design as desired to address locally-important
issues and to exploit expertise and other resources available to local
sites.
3. Within the first five years of the study, establish cooperative
relationships, identify and establish network research sites, collect
baseline data, implement initial treatments, document treatment costs
and short-term responses to treatments, report results, and designate
FFS research sites as demonstration areas for technology transfer to
professionals and for the education of students and the public.
4. Develop and maintain an integrated and spatially-referenced
database format to be used to archive data for all network sites,
facilitate the development of interdisciplinary and multi-scale
models, and integrate results across the network.
5. Identify and field test, in concert with resource managers and
users, a suite of response variables or measures that are: (a)
sensitive to the fire and fire surrogate treatments, and (b) both
technically and logistically feasible for widespread use in management
contexts. This suite of measures will form much of the basis for
management monitoring of operational treatments designed to restore
ecological integrity and reduce wildfire hazard.
6. Over the life of the study, quantify the ecological and economic
consequences of fire and fire surrogate treatments in a number of
forest types and conditions in the United States. Develop and validate
models of ecosystem structure and function, and successively refine
recommendations for ecosystem management.
Research Approach
Experimental Design
The benefits of an integrated study with multiple experimental sites
located around the country clearly can be enhanced if a common or
"core" experimental design is utilized. The core experimental
design for the FFS study--i.e., those elements of the design common to
all research sites in the network--consists of common (1) treatments,
(2) replication and plot size, and (3) response variables.
1. Treatments.
The following suite of four FFS treatments will be implemented at
each research site:
- untreated control
- prescribed fire only, with periodic reburns
- initial and periodic cutting, each time followed by mechanical
fuel treatment and/or physical removal of residue; no use of
prescribed fire
- initial and periodic cutting, each time followed by prescribed
fire; fire alone also could be used one or more times between
cutting intervals
These four treatments span a useful range both in terms of realistic
management options and anticipated ecological effects. The non-control
FFS treatments (treatments 2, 3, and 4) must be guided by a desired
future condition (DFC) or target stand condition. The DFC will be
defined mainly in terms of the tree component of the
ecosystem--specifying such targets as diameter distribution, species
composition, canopy closure, and spatial arrangements--and live and dead
fuel characteristics. The following fire-related minimum standard will
serve as a starting point for DFCs throughout the FFS network:
Each non-control treatment shall be designed to achieve stand and
fuel conditions such that, if impacted by a head fire under 80th
percentile weather conditions, at least 80 percent of the basal area of
overstory (dominant and codominant) trees will survive. (See full
proposal for further details.)
Given that this starting point is met for a given research site,
however, the DFC can and should incorporate any additional management
goals appropriate to the site and stand conditions and the expectations
of resource managers and other stakeholders. Beyond the fire-related
minimum standard for DFCs and the general treatment definitions given
above, it is neither feasible nor desirable to prescribe detailed
definitions of a core DFC or detailed treatment specifications that
would apply across all research sites. Participants at each research
site must provide this detail to ensure consistent application of
treatments at that site.
2. Replication and Unit Size.
Each treatment will be replicated at least 3 times at each research
site, using either a completely randomized or randomized block design as
appropriate to the research site. The core set of 4 treatments thus will
be represented in 12 treatment units at a research site. Each of the 12
core treatment units at a research site will be 10-ha, within which core
variables will be measured, surrounded by a buffer. The buffer, which is
to be treated in the same way as the treatment unit it surrounds, will
have a width at least equal to the height of a best site potential tree.
Where feasible, the replicated units will be supplemented by much larger
(200 to 400 ha or more), generally unreplicated areas treated to the
same specifications, to facilitate the study of larger-scale ecological
and economic/operational questions.
3. Response Variables.
A major aspect of the common design proposed for this study is a set
of core response variables to be measured at all the research sites.
Core variables encompass several broad disciplinary areas, including
vegetation, fuel and fire behavior, soils and forest floor, wildlife,
entomology, pathology, and treatment costs and utilization economics. (A
social science component probably will be linked to the study through
no-cost cooperative arrangements and/or non-JFSP funding.) A
corresponding set of disciplinary groups has had the responsibility for
developing the core variables and associated measurement protocols,
including coordinating across groups to ensure
consistency, compatibility, and non-duplication of data collection
efforts. Within-unit sampling of all variables will be keyed to a 50-m
square grid of permanent sample points to be established and maintained
in each treatment unit. Spatial referencing of all data to the grid will
facilitate both spatial and cross-disciplinary analyses.
As suggested in Project Objective #2, the overall study is designed
to balance the values of an integrated national network of research
sites having a common design against the needs for each site to retain
flexibility in addressing important local issues and in exploiting
expertise and other resources available to that site. Accordingly, at
the discretion of investigators, managers, and other participants
involved in a given site, the core design may be augmented (provided it
is not compromised) at that site by adding FFS treatments, adding one or
more DFCs, adding replications, increasing treatment unit size (by
increasing buffer width; the 10-ha treatment unit and core data
collected within it would remain unchanged), and/or adding response
variables. Except where additions to the core design are specifically
justified for a given research site, we are requesting support through
the Fire Science Program only for implementing the core design at each
site.
Research Site Locations
In selecting research sites we developed and used the following set
of criteria:
1. Site is representative of forests with a historically
short-interval, low- to moderate-severity fire regime and a currently
high risk of uncharacteristically severe fire.
2. Site is representative of widespread forest conditions (site
characteristics, forest type and structure, treatment history) that
are in need of, and likely to benefit from, fire or fire surrogate
treatments, and in which such treatments are feasible.
3. Site contributes significantly to balancing the overall network
in terms of regional representation and/or land ownership type.
4. Partners and cooperators are committed to and capable of
participating in the program. This involves several factors,
including: active support and interest in involvement on the part of
partners/cooperators; available land base for the study; ability and
willingness of land managers to implement the full suite of
experimental treatments successfully within required time frame,
repeat treatments over time as appropriate, commit selected sites for
long-term research uses, and document these commitments in amendments
to long-term land management plans.
5. On federal lands, treatment costs are borne by lead agency or
partner.
6. Partnerships exist across agencies and with universities, and
between researchers and managers.
The proposed initial network comprises 10 main sites and 1 satellite
site (satellite will have less than the full suite of core treatments):
1. Mission Creek, north-central Washington, Wenatchee National
Forest.
2. Hungry Bob, Blue Mountains of northeast Oregon, Wallowa-Whitman
National Forest.
3. Lubrecht Forest, University of Montana, northern Rockies,
western Montana.
4. Klamath Mountains, northwestern California, one or more national
forests, possibly other ownerships.
5. Blodgett Forest Research Station, University of
California-Berkeley, central Sierra Nevada, California.
6. Sequoia National Park, southern Sierra Nevada, California
(satellite to Blodgett Forest Research Station site).
7. Southwest Plateau, Coconino and Kaibab National Forests,
northern Arizona.
8. Jemez Mountains, Santa Fe National Forest, northern New Mexico.
9. Ohio Hill Country, lands managed by the Wayne National Forest,
the Ohio Division of Forestry, Mead Paper Corporation, and The Nature
Conservancy, southern Ohio.
10. Southeastern Piedmont, Clemson Experimental Forest,
northwestern South Carolina.
11. Florida Coastal Plain, Myakka River State
Park, southwest Florida.
All of these initial sites represent forests with a historically
short-interval, low- to moderate-severity fire regime. Eight sites are
in western coniferous forests, ranging from the Pacific Northwest to the
Southwest. These sites share the fact that ponderosa pine is an
important tree component, but sites vary in composition of other
conifers and differ substantially in topographic and soil parameters.
Two sites are in the southeastern U.S.--one in the Piedmont and one on
the Coastal Plain--and are dominated by mixtures of southern pines with
hardwood understories. Rounding out the network is a site in the
midwestern oak-hickory type of Ohio. Collectively, these sites comprise
a network that is truly national in scope. Depending on the level of
interest and support available, future sites in the same or other fire
regimes may be added to the network.
|