King Fire Restoration Project, Eldorado National Forest, Placer and El Dorado Counties, California, 77445-77447 [2014-30158]
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Federal Register / Vol. 79, No. 247 / Wednesday, December 24, 2014 / Notices
219 Subpart B). The administrative
review process provides an individual
or entity an opportunity for an
independent Forest Service review and
resolution of issues before the final
approval of a plan, plan amendment or
plan revision.
ADDRESSES: Written comments or
questions concerning this notice should
be addressed to Rio Grande National
Forest, Attn.: Plan Revision, 1803 W.
Hwy 160, Monte Vista, CO 81144, or by
email to: comments-rocky-mountain-riogrande@fs.fed.us (subject heading titled
Forest Plan Revision).
FOR FURTHER INFORMATION CONTACT:
Amy Waring, Forest Planner, (719) 852–
6215. Individuals who use
telecommunication devices for the deaf
(TDD) may call the Federal Information
Relay Service (FIRS) at 1–800–877–8339
between 5 a.m. and 5 p.m., Pacific Time,
Monday through Friday. More
information on the planning process can
also be found on the Rio Grande
National Forest Web site at https://www.
fs.usda.gov/riogrande.
SUPPLEMENTARY INFORMATION: The
National Forest Management Act
(NFMA) of 1976 requires that every
National Forest System (NFS) unit
develop a land management plan. On
April 9, 2012, the Forest Service
finalized its land management planning
rule (2012 Planning Rule), which
provides broad programmatic direction
to National Forests and National
Grasslands for developing and
implementing their land management
plans. Forest plans describe the strategic
direction for management of forest
resources for fifteen to twenty years, and
are adaptive and amendable as
conditions change over time.
Under the 2012 Planning Rule, the
assessment of ecological, social, and
economic trends and conditions is the
first stage of the planning process. The
second stage is a development and
decision process guided, in part, by the
NEPA and includes the preparation of a
draft environmental impact statement
and revised Forest Plan for public
review and comment, and the
preparation of the final environmental
impact statement and revised Forest
Plan. The third stage of the process is
monitoring and feedback, which is
ongoing over the life of the revised
forest plans.
With this notice, the agency invites
other governments, non-governmental
parties, and the public to contribute to
the development of the assessment
report. The assessment will rapidly
evaluate the sustainability of existing
ecological, economic, and social
conditions and trends within the
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context of the broader landscape. It will
help inform the planning process
through the use of Best Available
Scientific Information, while also taking
into account other forms of knowledge,
such as local information, national
perspectives, and native knowledge.
Lastly, the assessment will help identify
the need to change the existing 1996
plan.
Collaboration as part of the
assessment phase supports the
development of relationships of key
stakeholders throughout the plan
revision process, and is an essential step
to understanding current conditions,
available data, and feedback needed to
support a strategic, efficient planning
process. As public meetings, other
opportunities for public engagement,
and public review and comment
opportunities are identified to assist
with the development of the forest plan
revision, public announcements will be
made, notifications will be posted on
the Forest’s Web site at https://www.fs.
usda.gov/riogrande, and information
will be sent out to the Forest’s mailing
list. If anyone is interested in being on
the Forest’s mailing list to receive these
notifications, please contact Amy
Waring, Forest Planner, at the mailing
address identified above, by sending an
email to: comments-rocky-mountain-riogrande@fs.fed.us (subject heading titled
Forest Plan Revision).
Responsible Official: The responsible
official for the revision of the land
management plan for the Rio Grande
National Forest is Dan Dallas, Forest
Supervisor, Rio Grande National Forest,
1803 W. Hwy 160, Monte Vista, CO
81144.
Dated: December 17, 2014.
Dan S. Dallas,
Forest Supervisor, Rio Grande National
Forest.
[FR Doc. 2014–30189 Filed 12–23–14; 8:45 am]
BILLING CODE 3410–11–P
DEPARTMENT OF AGRICULTURE
Forest Service
King Fire Restoration Project,
Eldorado National Forest, Placer and
El Dorado Counties, California
Forest Service, USDA.
Notice of intent to prepare an
environmental impact statement.
AGENCY:
ACTION:
The Eldorado National Forest
proposes to restore portions of the King
Fire of 2014. The proposed action
includes hazard tree removal, fuel
reduction, salvage logging, reforestation,
SUMMARY:
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77445
road improvements, watershed
improvements, and research.
DATES: Comments concerning the scope
of the analysis must be received by
January 23, 2015. The draft
environmental impact statement is
expected March 2015 and the final
environmental impact statement is
expected June 2015.
ADDRESSES: Send written comments to
100 Forni Road, Placerville, CA 95667,
Attention: King Fire Restoration Project.
Comments may also be sent via email to
comments-pacificsouthwest-eldorado@
fs.fed.us, or via facsimile to 530–621–
5297.
FOR FURTHER INFORMATION CONTACT:
Patricia Ferrell, Team Leader, Eldorado
National Forest, 100 Forni Road,
Placerville, CA 95667, phone 530–642–
5146 or email to pferrell@fs.fed.us. A
scoping package, maps and other
information are online at: https://www.fs.
fed.us/nepa/nepa_project_exp.php
?project=45952.
Individuals who use
telecommunication devices for the deaf
(TDD) may call the Federal Information
Relay Service (FIRS) at 1–800–877–8339
between 8 a.m. and 8 p.m., Eastern
Time, Monday through Friday.
SUPPLEMENTARY INFORMATION:
General Background
The King Fire started September 13,
2104 and burned approximately 97,000
acres on the Eldorado National Forest
and on private timberlands. The project
area for this analysis is the
approximately 63,000 acre portion of
the King Fire on Eldorado National
Forest lands within the Georgetown,
Pacific, and Placerville Ranger Districts
administrative boundary. The project
area includes all or portions of 30
watersheds. The large high severity
portions of this fire resulted in adverse
effects to forest resources such as soil,
riparian areas, and wildlife habitat, and
killed thousands of trees that contribute
to hazardous conditions for people and
extremely high fuel loading over time.
Purpose and Need for Action
The underlying need(s) for this
proposal include: Reduce the risk from
falling dead, dying, and defective trees
to the safety of forest visitors and
workers, and of damaging private
property, structures, and cultural
resources; reduce accumulation of fuel
over the long term in strategic fire
management areas for the purpose of
improving the ability to manage and
control future fires; maintain the
ecological integrity of post fire habitat
while restoring diverse conifer forests
and laying the foundation for resiliency
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into the future; expeditiously recover
timber killed by the fire commensurate
with available markets, for the purpose
of generating funds to offset the cost of
restoration activities and contribute to
societal needs for wood products; take
advantage of research opportunities to
increase knowledge regarding the effects
of large fires on the environment, how
to reduce the risk of future fires, and
how to restore resilient forests after
fires; reduce existing and potential
sources of soil movement and
sedimentation to streams, and reduce
large woody fuel accumulation in
sensitive areas where a future fire is
likely to have detrimental effects on
soil, water, and cultural resources.
Proposed Action
In developing the proposed action,
consideration was given to areas that
burned with high severity outside the
natural range of variation; exclusion of
hardwood/shrub/grassland areas that
would continue to persist without
treatment; maximizing the probability of
California spotted owl persistence
within and adjacent to the King Fire,
maintaining habitat suitable for fire
obligate wildlife including the blackbacked woodpecker, promoting a
mosaic of post-fire vegetation important
for species associated with early seral
habitats, and minimizing impacts to the
threatened Sierra Nevada yellow-legged
frog and California red-legged frog;
conifer seed dispersal and the need to
plant trees in areas unlikely to naturally
regenerate; identification of wildland
urban interface defense zones where the
focus is on protecting life and property;
strategic fuel management zones to
contain wildfire and facilitate
prescribed fire; and generally eliminate
steep slopes from the proposed action
where treatments would be
prohibitively expensive, and where
treatment was not needed to meet other
objectives of the project.
Areas identified for treatment are:
approximately 1,200 acres in the
wildland urban interface (WUI) defense
zone where increasing fuel loads pose a
hazard to community fire protection;
approximately 7,300 acres within the
fire management zone which are
strategic areas identified to establish a
safe and effective place for future fire
suppression; approximately 5,600 acres
in the forest resiliency area where
reestablishment of conifer forests are
desired, ecologically sustainable, and
can be managed to have a high
probability of surviving subsequent
wildfire; other specific areas where
treatment would occur for research and
watershed improvement; and roads
needing hazard tree removal
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(approximately 429 miles), repair,
closure, and/or decommissioning.
Within Strategic Fuels Management
Zones, WUI Defense Zones, and Forest
Resiliency Areas, remove dead conifer
trees using in excess of soil cover needs
and wildlife snag retention levels needs.
In the Forest Resiliency Areas, snags
will generally be retained in two to five
acre patches covering 15 to 20 percent
of a treatment area and incorporating
the largest snags available. No standing
snags will be retained in WUI Defense
Zones, and four large snags per acre up
to 12sq. ft./acre basal area in a grouped
configuration will be retained in
Strategic Fire Management Zones. Trees
to be removed have brown foliage or no
foliage remaining as viewed from the
ground. Mortality monitoring for tree
removal may be conducted up to 4 years
following the fire.
Within Hazard Areas, remove hazard
trees along Forest Service system roads
open to the public and roads needed for
access to treatment areas, along private
residential property, adjacent to
structures, and in specific cultural
resource sites identified by the
archeologist. Hazard trees to be removed
are dead and dying trees that have
potential to reach the road or property
and live trees that are sufficiently
damaged or defective to pose a risk of
falling within the next 5 years.
Methods include mechanical or other
ground based logging on approximately
11,800 acres, skyline or helicopter
logging on approximately 700 acres,
hand treatments on approximately 700
acres, and mastication or machine piling
on approximately 100 acres.
In areas identified above, the
maximum desired surface fuel loading
is 6–10 tons per acre of material <3″
diameter. In areas described above
where additional treatment is needed to
reduce fuel loading to the desired level
or provide additional soil cover, tops,
limbs, and unmerchantable boles of
harvested trees, and small dead trees
that are not removed using the logging
methods described, would be treated by
one or more of the following methods:
cutting and scattering to within 18
inches of the ground, cutting and left in
place, hand piling, mastication or
chipping with a track mounted
masticator or chipper; and/or cutting
trees and piling using tractors or rubber
tired machinery with brush rakes or
grapples. Piles would be burned.
Within portions of watersheds
determined to be at high risk of soil
erosion and sedimentation which could
negatively impact watershed resources,
treatments include: Increasing
groundcover using onsite or imported
material (e.g. mastication, lop and
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scatter, mulching), obliteration of
existing disturbances, and removal of
excess woody material.
Planting of seedlings would occur on
approximately 14,000 acres of conifer
forest types where a forested community
is the desired condition, but where
natural regeneration of a desired species
composition and density are not
expected to occur within the next
several decades, and where stands can
reasonably be effectively and efficiently
managed into the future. Planting
strategies would be designed to
maintain ecological integrity while
balancing future climate projections,
economics, long-term management
feasibility, and desired conditions.
Except in the limited circumstances
where site preparation to treat residual
fuels is not needed, salvage logging
would be completed before planting
takes place. At the time of planting, the
planted seedlings would be released
from competing vegetation by hand
scraping a radius of 2 to 5 feet around
the seedlings depending on competing
vegetation and follow-up treatment
planned. Follow-up manual and
herbicide release of seedlings from
competing vegetation would occur
where competing vegetation is expected
to reduce seedling survival or growth
below an acceptable level. Proposed
research projects are to study the effect
of varying salvage and re-planting
intensities on the fuel complex and
native/non-native species abundance
over time; study forest resilience after
high-severity wildfire: the effect of snag
density and distribution on the
retention of forest ecosystem functions;
and additional projects to be
determined.
Responsible Official
Forest Supervisor, Eldorado National
Forest.
Nature of Decision To Be Made
The decision to be made is whether to
adopt and implement the proposed
action, an alternative to the proposed
action, or take no action to restore the
King Fire area.
Scoping Process
This notice of intent initiates the
scoping process, which guides the
development of the environmental
impact statement. A scoping open house
will be held January 13, 2015 in
Placerville, CA. Comments specific to
the location, methods, and actions
proposed are the most helpful.
It is important that reviewers provide
their comments at such times and in
such manner that they are useful to the
agency’s preparation of the
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environmental impact statement.
Therefore, comments should be
provided prior to the close of the
comment period and should clearly
articulate the reviewer’s concerns and
contentions.
Comments received in response to
this solicitation, including names and
addresses of those who comment, will
be part of the public record for this
proposed action. Comments submitted
anonymously will be accepted and
considered, however.
Dated: December 18, 2014.
Laurence Crabtree,
Forest Supervisor.
N. Mission Street, Building 2, McCall,
Idaho 83638. Comments may also be
sent via email to comments-intermtnpayette@fs.fed.us, or via facsimile to
208–634–0744.
FOR FURTHER INFORMATION CONTACT:
Stephen Penny, Project Team Leader,
208–253–0164, spenny@fs.fed.us.
Individuals who use telecommunication
devices for the deaf (TDD) may call the
Federal Information Relay Service
(FIRS) at 1–800–877–8339 between 8
a.m. and 8 p.m., Eastern Time, Monday
through Friday.
SUPPLEMENTARY INFORMATION:
Purpose and Need for Action
[FR Doc. 2014–30158 Filed 12–23–14; 8:45 am]
The purpose is to: (1) Move vegetation
toward the desired conditions (e.g.,
canopy closure in large tree class,
species composition, and size class
DEPARTMENT OF AGRICULTURE
distribution) defined in the Forest Plan
and consistent with the current science
Forest Service
for restoration of ponderosa pine,
Intermountain Region, Payette National Douglas-fir, grand fir, subalpine fir and
Forest, Council Ranger District, Idaho, lodgepole habitat types, with an
Middle Fork Weiser River Landscape
emphasis on: (a) Improving habitat for
Restoration Project
specific wildlife species of concern,
such as the species dependent on dry
AGENCY: Forest Service, USDA.
coniferous forests, while maintaining
ACTION: Notice of intent to prepare an
habitat for federally-listed and sensitive
environmental impact statement.
species; (b) Maintaining and promoting
large tree forest structure, early seral
SUMMARY: The Council Ranger District of
the Payette National Forest will prepare species composition (for example aspen,
western larch, ponderosa pine, and
an Environmental Impact Statement
Douglas-fir) and forest resiliency to fire,
(EIS) for the Middle Fork Weiser River
insects and disease and climate change;
Landscape Restoration Project. The
(c) Reducing the risk of uncharacteristic
Middle Fork Weiser River Landscape
wildland fire, with an emphasis on
Restoration Project area is located
restoring and maintaining desirable
approximately six miles southeast of
Council, Idaho, primarily in the Middle plant community attributes including
fuel levels, fire regimes, and other
Fork Weiser River watershed. It
ecological processes; and (d)
comprises approximately 50,000 acres
Maintaining and promoting large trees
and is within the boundaries of the
where retention is consistent with the
Council Ranger District of the Payette
above objectives. (2) Maintaining and
National Forest, in Adams County
promoting legacy ponderosa pine and
Idaho. The project is designed to move
western larch and legacy-like Douglas
vegetation toward desired conditions,
fir; (3) Restore heterogeneous fine and
improve wildlife habitat, reduce forest
landscape scale mosaic patterns by
fuels, improve watershed conditions
establishing varying patch sizes
through a variety of activities including
consistent with spatial patterns that
commercial and non-commercial
vegetation management and road system promote forest resilience to disturbance;
(4) Within dry non-forested habitats,
modifications and maintenance;
maintain and promote native grasses
improve recreation infrastructure and
and restore desired conditions for age
opportunities; and improve firefighter
and canopy class structure on sagebrush
and public safety by establishing
and bitterbrush; (5) Decrease the conifer
fuelbreaks.
encroachment into aspen and nonDATES: Comments concerning the scope
forested habitats; (6) In order of priority,
of the analysis must be received by
move the Granite Creek subwatershed
January 23, 2015. The draft
from a Watershed Condition Framework
environmental impact statement is
(WCF) rating of Class 3 (Impaired) to a
expected August, 2015 and the final
Class 2 (Functioning at Risk), and move
environmental impact statement is
Mica Creek, Jungle Creek, and Little Fall
expected February 2016.
Creek subwatersheds within the Project
area toward the desired condition for
ADDRESSES: Send written comments to
soil, water, riparian, and aquatic
Keith Lannom, Forest Supervisor, 500
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77447
resources; (7) Manage recreation use in
the Project with an emphasis on
hardening primary dispersed recreation
areas, improving existing trails and
providing new trail opportunities
including an OHV loop and a nonmotorized trail; (8) Contribute to the
economic vitality of the communities
adjacent to the Payette National Forest;
and (9) Improve firefighter and public
safety by establishing strategically
placed defensible fuelbreaks within the
Project area.
The need for the Project is based on
the difference between the existing and
desired conditions. These differences
include: (1) Loss of habitat for Family 1
wildlife species, such as the whiteheaded woodpecker, compared to
historical conditions; (2) Fewer large
tree size classes than desired in the drier
forest types (Potential Vegetation
Groups 2, and 5), and higher canopy
cover; (3) Fewer early seral tree species
(i.e. aspen, ponderosa pine and western
larch) than desired; (4) Increased stand
and landscape homogeneity of size
classes, species diversity, tree
distributions and canopy closure; (5)
Increased high canopy closer in the
large size classes in some vegetation
types; (6) Increased conifer
encroachment into aspen and nonforested habitats; (7) Fewer fire resistant
tree species (i.e., ponderosa pine and
Western larch) and higher densities of
non-fire resistant tree species; (8) Higher
surface fuel loading in those areas that
have missed one or more fire return
intervals; (9) Less than desired
watershed function and integrity,
including increased sedimentation,
hydrologic risk from flooding,
disturbance in RCAs (mainly roadrelated), habitat fragmentation, lack of
large woody debris in some streams, and
lack of coarse woody debris in areas of
past timber harvest; and (10) Trail and
recreation facilities that do not meet
current design and accessibility
standards.
Proposed Action
The Proposed Action includes: Up to
13,002 acres of commercial harvests (a
combination of Free Thin, Free Thin–
Patch Cut-Selection Harvest, Aspen
Restoration, and Mature Plantation
Harvest). Combined commercial and
non-commercial vegetation treatments
include up to 5,280 acres of Meadow
Restoration and 1,267 acres of
Restoration of Low Density Timber
Stands. Non-commercial treatments
include thinning up to 4,309 acres.
These acreages include treatments
designed for and within Riparian
Conservation Areas (RCAs) and total
approximately 3,428 acres. Prescribed
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Agencies
[Federal Register Volume 79, Number 247 (Wednesday, December 24, 2014)]
[Notices]
[Pages 77445-77447]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2014-30158]
-----------------------------------------------------------------------
DEPARTMENT OF AGRICULTURE
Forest Service
King Fire Restoration Project, Eldorado National Forest, Placer
and El Dorado Counties, California
AGENCY: Forest Service, USDA.
ACTION: Notice of intent to prepare an environmental impact statement.
-----------------------------------------------------------------------
SUMMARY: The Eldorado National Forest proposes to restore portions of
the King Fire of 2014. The proposed action includes hazard tree
removal, fuel reduction, salvage logging, reforestation, road
improvements, watershed improvements, and research.
DATES: Comments concerning the scope of the analysis must be received
by January 23, 2015. The draft environmental impact statement is
expected March 2015 and the final environmental impact statement is
expected June 2015.
ADDRESSES: Send written comments to 100 Forni Road, Placerville, CA
95667, Attention: King Fire Restoration Project. Comments may also be
sent via email to comments-pacificsouthwest-eldorado@fs.fed.us, or via
facsimile to 530-621-5297.
FOR FURTHER INFORMATION CONTACT: Patricia Ferrell, Team Leader,
Eldorado National Forest, 100 Forni Road, Placerville, CA 95667, phone
530-642-5146 or email to pferrell@fs.fed.us. A scoping package, maps
and other information are online at: https://www.fs.fed.us/nepa/nepa_project_exp.php?project=45952.
Individuals who use telecommunication devices for the deaf (TDD)
may call the Federal Information Relay Service (FIRS) at 1-800-877-8339
between 8 a.m. and 8 p.m., Eastern Time, Monday through Friday.
SUPPLEMENTARY INFORMATION:
General Background
The King Fire started September 13, 2104 and burned approximately
97,000 acres on the Eldorado National Forest and on private
timberlands. The project area for this analysis is the approximately
63,000 acre portion of the King Fire on Eldorado National Forest lands
within the Georgetown, Pacific, and Placerville Ranger Districts
administrative boundary. The project area includes all or portions of
30 watersheds. The large high severity portions of this fire resulted
in adverse effects to forest resources such as soil, riparian areas,
and wildlife habitat, and killed thousands of trees that contribute to
hazardous conditions for people and extremely high fuel loading over
time.
Purpose and Need for Action
The underlying need(s) for this proposal include: Reduce the risk
from falling dead, dying, and defective trees to the safety of forest
visitors and workers, and of damaging private property, structures, and
cultural resources; reduce accumulation of fuel over the long term in
strategic fire management areas for the purpose of improving the
ability to manage and control future fires; maintain the ecological
integrity of post fire habitat while restoring diverse conifer forests
and laying the foundation for resiliency
[[Page 77446]]
into the future; expeditiously recover timber killed by the fire
commensurate with available markets, for the purpose of generating
funds to offset the cost of restoration activities and contribute to
societal needs for wood products; take advantage of research
opportunities to increase knowledge regarding the effects of large
fires on the environment, how to reduce the risk of future fires, and
how to restore resilient forests after fires; reduce existing and
potential sources of soil movement and sedimentation to streams, and
reduce large woody fuel accumulation in sensitive areas where a future
fire is likely to have detrimental effects on soil, water, and cultural
resources.
Proposed Action
In developing the proposed action, consideration was given to areas
that burned with high severity outside the natural range of variation;
exclusion of hardwood/shrub/grassland areas that would continue to
persist without treatment; maximizing the probability of California
spotted owl persistence within and adjacent to the King Fire,
maintaining habitat suitable for fire obligate wildlife including the
black-backed woodpecker, promoting a mosaic of post-fire vegetation
important for species associated with early seral habitats, and
minimizing impacts to the threatened Sierra Nevada yellow-legged frog
and California red-legged frog; conifer seed dispersal and the need to
plant trees in areas unlikely to naturally regenerate; identification
of wildland urban interface defense zones where the focus is on
protecting life and property; strategic fuel management zones to
contain wildfire and facilitate prescribed fire; and generally
eliminate steep slopes from the proposed action where treatments would
be prohibitively expensive, and where treatment was not needed to meet
other objectives of the project.
Areas identified for treatment are: approximately 1,200 acres in
the wildland urban interface (WUI) defense zone where increasing fuel
loads pose a hazard to community fire protection; approximately 7,300
acres within the fire management zone which are strategic areas
identified to establish a safe and effective place for future fire
suppression; approximately 5,600 acres in the forest resiliency area
where reestablishment of conifer forests are desired, ecologically
sustainable, and can be managed to have a high probability of surviving
subsequent wildfire; other specific areas where treatment would occur
for research and watershed improvement; and roads needing hazard tree
removal (approximately 429 miles), repair, closure, and/or
decommissioning.
Within Strategic Fuels Management Zones, WUI Defense Zones, and
Forest Resiliency Areas, remove dead conifer trees using in excess of
soil cover needs and wildlife snag retention levels needs. In the
Forest Resiliency Areas, snags will generally be retained in two to
five acre patches covering 15 to 20 percent of a treatment area and
incorporating the largest snags available. No standing snags will be
retained in WUI Defense Zones, and four large snags per acre up to
12sq. ft./acre basal area in a grouped configuration will be retained
in Strategic Fire Management Zones. Trees to be removed have brown
foliage or no foliage remaining as viewed from the ground. Mortality
monitoring for tree removal may be conducted up to 4 years following
the fire.
Within Hazard Areas, remove hazard trees along Forest Service
system roads open to the public and roads needed for access to
treatment areas, along private residential property, adjacent to
structures, and in specific cultural resource sites identified by the
archeologist. Hazard trees to be removed are dead and dying trees that
have potential to reach the road or property and live trees that are
sufficiently damaged or defective to pose a risk of falling within the
next 5 years.
Methods include mechanical or other ground based logging on
approximately 11,800 acres, skyline or helicopter logging on
approximately 700 acres, hand treatments on approximately 700 acres,
and mastication or machine piling on approximately 100 acres.
In areas identified above, the maximum desired surface fuel loading
is 6-10 tons per acre of material <3 diameter. In areas
described above where additional treatment is needed to reduce fuel
loading to the desired level or provide additional soil cover, tops,
limbs, and unmerchantable boles of harvested trees, and small dead
trees that are not removed using the logging methods described, would
be treated by one or more of the following methods: cutting and
scattering to within 18 inches of the ground, cutting and left in
place, hand piling, mastication or chipping with a track mounted
masticator or chipper; and/or cutting trees and piling using tractors
or rubber tired machinery with brush rakes or grapples. Piles would be
burned.
Within portions of watersheds determined to be at high risk of soil
erosion and sedimentation which could negatively impact watershed
resources, treatments include: Increasing groundcover using onsite or
imported material (e.g. mastication, lop and scatter, mulching),
obliteration of existing disturbances, and removal of excess woody
material.
Planting of seedlings would occur on approximately 14,000 acres of
conifer forest types where a forested community is the desired
condition, but where natural regeneration of a desired species
composition and density are not expected to occur within the next
several decades, and where stands can reasonably be effectively and
efficiently managed into the future. Planting strategies would be
designed to maintain ecological integrity while balancing future
climate projections, economics, long-term management feasibility, and
desired conditions. Except in the limited circumstances where site
preparation to treat residual fuels is not needed, salvage logging
would be completed before planting takes place. At the time of
planting, the planted seedlings would be released from competing
vegetation by hand scraping a radius of 2 to 5 feet around the
seedlings depending on competing vegetation and follow-up treatment
planned. Follow-up manual and herbicide release of seedlings from
competing vegetation would occur where competing vegetation is expected
to reduce seedling survival or growth below an acceptable level.
Proposed research projects are to study the effect of varying salvage
and re-planting intensities on the fuel complex and native/non-native
species abundance over time; study forest resilience after high-
severity wildfire: the effect of snag density and distribution on the
retention of forest ecosystem functions; and additional projects to be
determined.
Responsible Official
Forest Supervisor, Eldorado National Forest.
Nature of Decision To Be Made
The decision to be made is whether to adopt and implement the
proposed action, an alternative to the proposed action, or take no
action to restore the King Fire area.
Scoping Process
This notice of intent initiates the scoping process, which guides
the development of the environmental impact statement. A scoping open
house will be held January 13, 2015 in Placerville, CA. Comments
specific to the location, methods, and actions proposed are the most
helpful.
It is important that reviewers provide their comments at such times
and in such manner that they are useful to the agency's preparation of
the
[[Page 77447]]
environmental impact statement. Therefore, comments should be provided
prior to the close of the comment period and should clearly articulate
the reviewer's concerns and contentions.
Comments received in response to this solicitation, including names
and addresses of those who comment, will be part of the public record
for this proposed action. Comments submitted anonymously will be
accepted and considered, however.
Dated: December 18, 2014.
Laurence Crabtree,
Forest Supervisor.
[FR Doc. 2014-30158 Filed 12-23-14; 8:45 am]
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