Purpose of the
Project and Proposed Action
February 5,
2004 FNF Press Release
BACKGROUND of
the FIRES
The West Side Reservoir Fires burned a total of approximately
30,000 acres on the Hungry Horse and Spotted Bear Ranger Districts
of the Flathead National Forest. Lightning storms on August 19,
2003, ignited a series of wildland fires scattered across
approximately 30 miles of the east facing-slope of the Swan Range
just west of the Hungry Horse Reservoir. Collectively known as the
West Side Reservoir Fires, individual fires occurred in four
separate fire groups: the Beta/Doris Complex, the Blackfoot
Complex, the Doe Complex, and the Ball Fire. Here is some basic
information about these fires, all of which burned only on
National Forest System lands:
A
Forest Service Burned Area Emergency Rehabilitation (BAER) team
was assigned in August 2003 to determine emergency watershed
rehabilitation needs created by the fires. Some of the needs
identified in their analysis included aerial tree seeding; shrub
planting; hazard tree removal along trails; cleaning road ditches,
culvert inlets, and catch basins; constructing diversion dips on
roads; and upgrading culverts. These actions began in late 2003
and will continue in the summer of 2004.
PURPOSE
of this PROJECT
The
purpose of the West Side Reservoir Post-Fire Project is to harvest
burned trees while it is still economically feasible to do so.
Timely recovery of wood fiber will support local communities and
contribute to the long-term yield of forest products. Past
experience with fire salvage in northwestern Montana indicates
that “whitewood species” such as spruce, subalpine fir,
lodgepole pine, and western white pine substantially deteriorate
within a year or so after a fire. Salvage operations would need to
be completed within one to two years to ensure economic
utilization of the whitewood species that burned in the West Side
Fires.
Western larch and Douglas-fir resist checking
and rot for a longer period of time, perhaps up to two or three
years. But because these more rot-resistant species do lose some
value immediately and are intermingled with whitewood species
within drainages in the proposed project area, it is most
cost-efficient to also begin harvesting these species in the next
year or two.
In general, the species composition of the
burned areas is mixed stands of spruce, Douglas-fir, and western
larch at the low to mid elevations. The high-elevation forests are
dominated by spruce and subalpine fir. Western white pine is an
occasional forest component primarily at lower elevations, and
lodgepole pine is found scattered throughout. Other species such
as western red cedar, grand fir, and birch are found in minor
quantities at low elevations.
In total, the West Side Reservoir Fires burned
approximately 30,000 acres distributed among the following burn
severities:
|
|
Percent of Total Area Burned
|
Description of Mortality
|
|
High
|
43%
|
|
|
Moderate
|
31%
|
30 to 80% of the trees were killed.
|
|
Low
|
26%
|
|
Some additional mortality is expected in all burn
severity areas. This delayed mortality is especially likely to
occur in whitewood species and in areas of low and moderate
vegetation burn severities where fire damaged many trees, but did
not kill them immediately.
PROPOSED ACTION
Salvage
Salvage harvest of dead trees and trees
damaged by the fire and likely to die would occur on a total of
approximately 6,138 acres (approximately 20% of the burned area)
within four fire groups (See attached maps):
|
Fire
|
Salvage Harvest
|
|
Beta/Doris
|
2159 acres
|
|
Blackfoot
|
1808 acres
|
|
Ball
|
1785 acres
|
|
Doe
|
386 acres
|
|
TOTAL
|
6138 acres
|
In developing the Proposed Action, the
Interdisciplinary Team proposes to salvage only those acres that
meet the following criteria:
•
In burned areas with dead trees.
•
Outside inventoried roadless areas and the Jewel Basin Hiking
Area.
•
Outside areas that currently meet old growth habitat.
•
Outside areas that have been regeneration harvested in the recent
past.
•
Outside riparian areas. An exception occurs on a relatively few
acres where burned riparian areas can be accessed by existing open
road; these acres would be harvested by helicopter. One reason why
these riparian acres are proposed for harvest is because future
firewood gathering by the public has the potential to cause
resource damage in these areas.
•
Within stands with enough timber volume to be merchantable
considering the harvest method appropriate for the soil type,
steepness of slope, and available transportation system.
The number of acres included in the Proposed
Action are the maximum that the Interdisciplinary Team considers
at this time to be reasonable candidates for salvage. Further
field surveys in the summer of 2004 may provide information that
will reduce the total number of acres proposed for salvage
harvest, may change the logging system proposed for particular
units, or may cause other unforeseen reductions in total acres.
The Proposed Action focuses on salvage mostly
within high and moderate vegetation burn severities:
|
|
|
|
|
High
|
2950
acres
|
48%
|
|
Moderate
|
2410
acres
|
40%
|
|
Low
|
780
acres
|
12%
|
Mostly dead or dying trees would be harvested in
all areas that burned. Some live trees may be cut to accommodate
landings, skid trails, skyline corridors, or for safety reasons.
Individual and variable sized patches of dead trees would be
maintained to provide adequate present and future amounts of
larger diameter standing/down trees across the landscape, or to
provide for site protection. A total of approximately 70 to 80
million board feet could be harvested, the exact amount depending
on merchantability at the time of harvest.
Logging methods to remove merchantable trees
would depend on slope and soil sensitivity, and would include
helicopter, cable, and tractor-type equipment such as crawler
tractors, skidders, feller/bunchers, and cut-to-length harvesters.
Impacts to the more severely burned soils would be minimized
through the use of helicopters, winter logging, or skidding on
slash mat materials (adequate amounts of available fine woody
debris). Up to 50 helicopter landing areas would be proposed and
reclaimed after harvest activities. Approximately 71% of the area
would be logged by helicopters, 17% by cable, and 12% by
tractor-type equipment.
Fuels Reduction and Planting Within
Salvage Units
After salvage harvest, fuel reduction
and site preparation activities are proposed for some units,
depending on soil resource concerns. Planting of native tree
seedlings would occur within some salvage units (approximately
1700 acres) after salvage harvest to return the site to fully
forested conditions in a timely manner and promote desired species
diversity in the future forest. Desired species to plant would be
western white pine, western larch, Douglas-fir, and Engelmann
spruce. Willow, alder, and other shrub species would be considered
for planting in riparian areas.
Roads Needed for Salvage Harvest
No new permanent system roads or
temporary roads would be constructed. Approximately 4.5 miles of
historic road templates would be temporarily used to provide
access to salvage harvest units (See attached maps). These
temporary roads would then be rehabilitated after logging
activities. Best Management Practices would be employed to
minimize soil erosion and protect water quality on those roads
used during salvage activities and in harvest units.
Compatibility of Salvage Harvest
with Flathead Forest Plan Direction
The majority of acres proposed for
salvage harvest are located in Forest Plan management areas (MAs)
that are suitable for long-term timber management: MAs 7, 15, 16,
and 17. Also proposed for salvage are a total of approximately 227
acres that are in MAs considered unsuitable for long-term timber
management, but where salvage is allowed. These MAs are:
MA
2A - unroaded lands suited for dispersed semi-primitive
non-motorized recreation (Doe and Blackfoot Fire Groups).
MA
2B - unroaded lands suited for dispersed semi-primitive motorized
recreation (Doe, Beta, Ball, and Blackfoot Fire Groups).
MA
12 - riparian areas consisting of aquatic, riparian, and a portion
of terrestrial ecosystems along most perennial streams, lakes,
ponds, marshlands, bogs and some important seasonal flow streams
(Beta, Ball, and Blackfoot Fire Groups).
Access Management Strategy
The proposed action would include activities
to change access management within the Ball Branch, Kah Soldier,
Wheeler Quintonkon, Jewel Basin Graves, Wounded Buck Clayton, and
Doris Lost Johnny grizzly bear subunits to reduce current open
motorized access density and total motorized access density, and
improve security core for grizzly bears (Refer to attached
existing and proposed access management maps). The West Side
Reservoir Fires affected all these subunits to some degree.
Amendment 19 to the Flathead Forest Plan
established new forest-wide objectives and standards for grizzly
bear security within the Flathead National Forest to meet
long-term conservation needs of this threatened species. Amendment
19 established standards for open motorized access density, total
motorized access density and security core area, in areas known as
grizzly bear management subunits (these grizzly bear subunits
approximate the size of the home range for an adult female grizzly
bear). The following describes these standards:
Amendment
19 Standards (Long-term)
Open
Motorized Access Density (<1 mi/mi2)
≤ 19%
Total
Motorized Access Density (<2 mi/mi2)
≤ 19%
Security
Core (>=2500 acres) ≥ 68%
Summary of Open Road Changes.
Approximately 20 miles of open yearlong/seasonally open road would
be closed yearlong to wheeled motorized vehicles within several of
the grizzly bear subunits (full compliance with Amendment 19’s
standards would have required 50 miles of open yearlong/seasonally
open road to be closed to wheeled motorized vehicles; 39 miles of
open road would need to be closed if more motorized trails were
closed). Some of the most notable changes in road status involved
with the proposed action are as follows:
A
yearlong closure to wheeled motorized vehicles on the Wounded Buck
Road 895C and Wildcat Road 5339.
A
yearlong closure to wheeled motorized vehicles on the Lid Creek
Road 2817.
A
yearlong closure to wheeled motorized vehicles on Road 9796 (north
of Graves Bay) that currently provides access to the Pioneer Ridge
trailhead. A 1-2 mile new connector trail would be constructed to
provide access to Trail 71 (Pioneer Ridge Trail).
A
seasonal opening to wheeled motorized vehicles from July 1 –
November 30 on the Aurora Basin Road (895H) to allow access to the
Doris Ridge trailhead.
Summary of Motorized Trail Changes.
Approximately 43 miles of trail currently open to motorized use
would be closed to wheeled motorized use yearlong (full compliance
with Amendment 19 standards would have required over 61 miles of
motorized trails to be closed yearlong; 49 miles of motorized
trail would need to be closed if more open roads were closed).
Some of the most notable proposed yearlong closures of trails
currently open to wheeled vehicles are as follows:
Trail
51 (Columbia Mountain to Hungry Horse).
Upper
Lost Johnny Basin motorized route.
Trail
297 – Jimmy Ridge.
Trail
7 - Alpine Trail from south of Strawberry Lake to Jewel Basin.
Trail
7 - Alpine Trail from south of Jewel Basin to Tom Tom Mountain.
Trail
396 - Connor Creek.
Road
547 - Sullivan Creek Road (currently open to motorcycle use).
Trail
410 – Forest Creek Trail (access to Margaret Lake).
Summary of Road Decommissioning. In
addition to changes to open roads, approximately 49 miles of road
would be decommissioned in several of the grizzly bear subunits
(full compliance of Amendment 19’s standards would have required
over 70 miles of roads to be decommissioned). All of these 49
miles of road decommissioning are currently closed to wheeled
motorized use yearlong, except for 0.8 miles that are currently
open yearlong. Almost half of the road decommissioning would occur
in the Wounded Buck Clayton grizzly bear subunit.
Road decommissioning would include actions
that would minimize the potential for future sedimentation of
streams or noxious weed development. These actions would include
placement of numerous waterbars, culvert removals, grass seeding,
slash or debris placement on roads, planting shrubs, physical
alteration of the road template, and/or spraying herbicides on
existing noxious weed infestations.
Culvert removals and stream restoration would
occur where roads to be decommissioned intersect streams. To
reduce the amount of ground disturbed, cross drain culverts would
typically not be removed, but waterbars would be placed nearby.
The amount of physical altering of the road template from culvert
removal or water bar creation would vary according to the sites
involved.
Project-Specific Amendment. The access
management strategy described above does not meet the 10-year
standards specified in the Forest Plan and would require a
project-specific Forest Plan amendment. The Forest Plan would be
amended to change open motorized access density, total motorized
access density and security core standards to the following
percentages in the Wheeler Quintonkon, Wounded Buck Clayton, and
Doris Lost Johnny grizzly bear subunits:
|
Grizzly
Bear Subunit
|
Open
Motorized Access Density
|
Total
Motorized Access Density
|
Security
Core
|
|
BALL BRANCH
|
|
Existing
|
20%
|
8%
|
76%
|
|
Proposed
|
12%
|
3%
|
82%
|
|
KAH SOLDIER
|
|
Existing
|
32%
|
22%
|
59%
|
|
Proposed
|
19%
|
19%
|
68%
|
|
WHEELER QUINTONKON
|
|
Existing
|
29%
|
24%
|
55%
|
|
Proposed
|
25%
|
19%
|
68%
|
|
JEWEL BASIN GRAVES
|
|
Existing
|
22%
|
24%
|
54%
|
|
Proposed
|
19%
|
19%
|
68%
|
|
WOUNDED BUCK CLAYTON
|
|
Existing
|
38%
|
42%
|
34%
|
|
Proposed
|
21%
|
29%
|
64%
|
|
DORIS LOST JOHNNY
|
|
Existing
|
60%
|
23%
|
31%
|
|
Proposed
|
44%
|
16%
|
55%
|
Note: shading indicates what Amendment 19
standards would be amended by the proposed action
This project-specific amendment would remain in place
pending completion of revision of the Flathead Forest Plan,
currently in progress and expected to be completed by 2006.
The scoping period is over for this
project and we are expecting the DEIS this summer or early Fall.