Special Areas; Roadless Area Conservation; National Forest System Lands in Alaska, 68688-68703 [2020-23984]
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DEPARTMENT OF AGRICULTURE
Forest Service
36 CFR Part 294
RIN 0596–AD37
Special Areas; Roadless Area
Conservation; National Forest System
Lands in Alaska
Forest Service, Agriculture
Department (USDA).
ACTION: Final rule and record of
decision.
AGENCY:
The U.S. Department of
Agriculture (USDA or Department), is
adopting a final rule to exempt the
Tongass National Forest from the 2001
Roadless Area Conservation Rule (2001
Roadless Rule), which prohibits timber
harvest and road construction/
reconstruction with limited exceptions
within designated inventoried roadless
areas. In addition, the rule directs an
administrative change to the timber
suitability of lands deemed unsuitable,
solely due to the application of the 2001
Roadless Rule, in the 2016 Tongass
National Forest Land and Resource
Management Plan (Tongass Forest Plan
or Forest Plan), Appendix A. The rule
does not authorize any grounddisturbing activities, nor does it increase
the overall amount of timber harvested
from the Tongass National Forest.
DATES: This rule is effective October 29,
2020.
FOR FURTHER INFORMATION CONTACT: Ken
Tu, Interdisciplinary Team Leader, at
303–275–5156 or akroadlessrule@
usda.gov. Individuals using
telecommunication devices for the deaf
(TDD) may call the Federal Information
Relay Services at 1–800–877–8339
between 8 a.m. and 8 p.m. Eastern Time,
Monday through Friday.
SUPPLEMENTARY INFORMATION: The USDA
Forest Service manages approximately
21.9 million acres of federal lands in
Alaska, which are distributed across two
national forests (Tongass and Chugach
National Forests). These national forests
are characterized by a diverse array of
landscapes, ecosystems, natural
resources, and land use activities.
In January 2001, the USDA
promulgated a discretionary rulemaking
establishing prohibitions on timber
harvesting and road construction on
approximately 58 million acres of the
National Forest System (NFS), including
over 14 million acres within Alaska.
The 2001 Roadless Rule has been the
subject of litigation for almost two
decades. Initially, the 2001 Roadless
Rule was challenged in multiple
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SUMMARY:
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lawsuits, including a suit brought by the
State of Alaska. Another suit filed by the
State of Alaska in 2015 is still ongoing.
Citing various concerns, including
damage to the economic and social
fabric of southeast Alaska and
compliance with the Alaska National
Interest Lands Conservation Act
(ANILCA) and Tongass Timber Reform
Act (TTRA), the State of Alaska
petitioned the USDA to exempt the
Tongass National Forest from the 2001
Roadless Rule.
Having carefully considered the
petition, public comments on the
proposed rule, and a wide range of
alternative approaches to the 2001
Roadless Rule, the USDA is granting the
State of Alaska’s request to exempt the
Tongass National Forest from the 2001
Roadless Rule. The Tongass Forest Plan
along with other conservation measures,
will assure protection allowing roadless
area values to prevail on the Tongass
National Forest while offering
additional flexibility to achieve other
multiple-use benefits.
Background
On January 12, 2001, the USDA
promulgated the Roadless Area
Conservation Rule (hereafter 2001
Roadless Rule) (66 FR 3244),
establishing nationwide prohibitions on
timber harvest, road construction, and
road reconstruction within inventoried
roadless areas (IRAs) with certain
limited exceptions. The intent of the
2001 Roadless Rule is to provide lasting
protection for IRAs within the NFS in
the context of multiple-use land
management. Based on the State of
Alaska’s Roadless Rule Petition
(described below) and a review of
public comment, the USDA analyzed
rulemaking alternatives addressing
whether and how the national
prohibitions on timber harvesting, road
construction, and road reconstruction
should apply on the Tongass National
Forest.
In 2001, the State of Alaska filed a
lawsuit challenging the USDA’s
promulgation of the 2001 Roadless Rule
and its application in Alaska. State of
Alaska v. USDA, A01–039 CV (JKS) (D.
Alaska). The USDA and the State of
Alaska reached a settlement in 2003,
and the USDA subsequently issued a
rule temporarily exempting the Tongass
National Forest from the 2001 Roadless
Rule. In 2011, a Federal district court set
aside the Tongass Exemption Rule and
reinstated, with clarifying instructions,
the 2001 Roadless Rule on the Tongass
National Forest. The district court’s
ruling was initially reversed by a threejudge panel of the Ninth Circuit but was
ultimately upheld in a 6–5 en banc
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ruling in 2015. Consequently, the 2001
Roadless Rule (as provided for in the
district court’s Judgment) remains in
effect in Alaska and the Forest Service
continues to apply the 2001 Roadless
Rule to both the Tongass and Chugach
National Forests.
Currently there are over 21.9 million
acres of NFS lands within the State of
Alaska, of which approximately 14.7
million acres (67%) are designated IRAs
as defined by the 2001 Roadless Rule,
including both the Tongass and
Chugach National Forests. The Tongass
National Forest is approximately 16.7
million acres of which approximately
9.3 million (55%) acres are designated
IRAs. The Alaska Roadless Rule focuses
on the Tongass National Forest only and
does not apply to the Chugach National
Forest.
State of Alaska Petition
In January 2018, then-Commissioner
of the Department of Natural Resources
for the State of Alaska, Andrew Mack
submitted a petition on behalf of the
State of Alaska to Secretary of
Agriculture Sonny Perdue pursuant to
the Administrative Procedure Act
(APA). The petition requested USDA
consider creation of a state-specific rule
to exempt the Tongass National Forest
from the 2001 Roadless Rule and
conduct a forest plan revision for the
Tongass National Forest. In June 2018,
the Secretary of Agriculture accepted
the petition and agreed to review the
State’s concerns on roadless area
management and economic
development opportunities in southeast
Alaska through a rulemaking process.
The Secretary directed the Forest
Service to begin working with
representatives from the State of Alaska
concerning a state-specific roadless rule.
However, the Secretary did not commit
to the State’s request for a forest plan
revision. On August 2, 2018, the State
of Alaska and the USDA Forest Service
signed a memorandum of understanding
concerning the development of a statespecific rule. The Forest Service
initiated its environmental analysis
process with the publication in the
Federal Register of a Notice of Intent
(NOI) to prepare an environmental
impact statement (EIS) on August 30,
2018 (83 FR 44252).
On September 6, 2018, Governor
Walker issued Administrative Order 299
to establish the Alaska Roadless Rule
Citizen Advisory Committee (the
committee) to provide an opportunity
for Alaskans to advise the State of
Alaska on the future management of
Tongass National Forest roadless areas.
The committee was comprised of 13
members, appointed by Governor
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Walker, intended to represent a
diversity of perspectives, including
Alaska Native tribes and corporations,
fishing, timber, conservation, tourism,
utilities, mining, transportation, local
government, and the Alaska Division of
Forestry. The committee’s specific task
was to present a written report on the
rulemaking process to the Governor and
State Forester, which included options
for a state-specific roadless rule. The
committee met for three in-person
meetings during the fall of 2018
(October 2–3 in Juneau; October 24–26
in Ketchikan; and November 6–8 in
Sitka). Meetings were open to the public
and each meeting included opportunity
for public comment. The committee’s
report was submitted to the Governor
and State Forester during late November
2018, and recommendations from the
committee informed the State of Alaska
input, as a cooperating agency, to the
Forest Service in the development of the
alternatives and comments on the Draft
Environmental Impact Statement (DEIS).
On October 17, 2019, the USDA
published a notice of proposed
rulemaking to exempt the Tongass
National Forest from the 2001 Roadless
Rule (84 FR 55522). The Office of
Federal Activities of the U.S.
Environmental Protection Agency
published a Notice of Availability
(NOA) for the DEIS in the Federal
Register on October 18, 2019 (84 FR
55952), with corrected end of comment
period published on October 25, 2019
(84 FR 57417).
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Consideration of the State of Alaska’s
Petition
In response to the State of Alaska’s
petition for rulemaking, the USDA has
sought a long-term, durable approach to
roadless area management that
accommodates the unique biological,
social, and economic situation found in
and around the Tongass National Forest.
The Tongass is unique from other
national forests with respect to size,
percentage of IRAs, number of
communities dependent on federal
lands (the Tongass comprises almost
80% of southeast Alaska and supports
32 communities), and Alaska and
Tongass-specific statutory
considerations (e.g., ANILCA, TTRA).
The USDA and Forest Service believe
that both roadless area conservation and
other multiple-use values with
important local socio-economic
consequences are meaningfully
addressed through local and regional
forest planning on the Tongass, without
the 2001 Roadless Rule prohibitions on
timber harvest and road construction/
reconstruction.
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Decision
The USDA hereby promulgates a
regulation exempting the Tongass
National Forest from the 2001 Roadless
Rule as described in Alternative 6 of the
Rulemaking for Alaska Roadless Areas
Final Environmental Impact Statement
(FEIS) (USDA Forest Service, 2020).
This decision is not subject to Forest
Service administrative review
regulations, which allow the public to
administratively challenge certain
agency decisions. In addition, the final
rule directs the Tongass Forest
Supervisor to issue a notice of an
administrative change pursuant to 36
CFR 219.13(c) to the timber suitability
determination as described in Appendix
A of the Forest Plan. The final
regulatory text differs slightly from the
text published with the FEIS, reflecting
nontechnical changes made to conform
to the Office of Federal Register’s
guidelines.
Alternatives Considered
In addition to Alternative 6, the
selected alternative, the FEIS analyzes
five other alternatives for managing
roadless areas on the Tongass National
Forest. Alternative 1 is the no action
alternative and would result in the
continued implementation of the 2001
Roadless Rule as prescribed in the
Alaska District Court’s Judgement.
Alternative 2 provides limited
additional timber harvest opportunity
while maximizing roadless area
designations. It removes approximately
142,000 acres from roadless designation
that have been substantially altered by
prior road construction or timber
harvest generally conducted during
periods of time the Tongass National
Forest was exempted from the 2001
Roadless Rule. These substantially
altered areas are generally known as
‘‘roaded roadless’’ acres, but include
additional areas considered to be
substantially altered. Alternative 2 also
adds 110,000 acres as Alaska Roadless
Areas. Following an approach similar to
that taken for the other two Statespecific roadless rules, Colorado and
Idaho, the FEIS uses the term Alaska
Roadless Areas to refer to the areas in
which the Alaska Roadless Rule would
apply in Alternatives 2 through 5.
Alternative 3 would increase the
available land base from which timber
harvest opportunities could occur by
making timber harvest, road
construction, and road reconstruction
permissible in areas where roadless
characteristics have already been
substantially altered and areas
immediately adjacent to existing roads
and past harvest areas. Adjacent areas
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are considered to be the logical
extensions of the existing road and/or
harvest systems, which would remove
approximately 401,000 acres from the
roadless classification system. The
adjacent areas represent the most likely
locations where future timber harvest
could occur and have the least
environmental impacts to overall
roadless characteristics while providing
for additional timber harvest
opportunities.
Alternative 3 also establishes a
Community Priority category which
allows for small-scale timber harvest
and associated road construction and
reconstruction. In addition, it allows for
infrastructure development to connect
and support local communities,
recreation opportunities, and traditional
Alaska Native cultural uses. Alternative
3 includes the Watershed Priority
category, which is more restrictive than
the 2001 Roadless Rule, and applied to
approximately 3.26 million acres
primarily identified in the Forest Plan
as the Tongass 77 Watersheds and The
Nature Conservancy/Audubon
Conservation Priority Areas (T77 and
The Nature Conservancy/Audubon
Conservation Areas) and high-priority
sockeye salmon watersheds.
Approximately 90% of those 3.26
million acres fall within roadless area
boundaries identified in Alternative 3.
To provide heightened balance and
integrity of watershed protections and
establish management continuity across
these high-priority watersheds,
Alternative 3 would also include a
prohibition on old-growth timber
harvesting on the portion of the T77 and
The Nature Conservancy/Audubon
Conservation Areas that extend beyond
roadless areas boundaries established by
Alternative 3. The remaining 4,595,000
acres of Alaska Roadless Areas in
Alternative 3 would be managed under
a roadless management category called
Roadless Priority, which is similar to
the 2001 Roadless Rule but less
restrictive and addresses Alaska-specific
concerns for infrastructure development
to connect and support local
communities and access to renewable
energy and leasable minerals.
In addition to roaded roadless and
adjacent acres being removed from the
roadless classification system,
approximately 854,000 acres designated
as land use designation (LUD) II areas
would be removed from the roadless
classification system in Alternative 3.
LUD II areas are statutory land use
designations managed in a roadless state
to retain their wildland character as
defined in the TTRA (Pub. L. 101–626,
Title II, Section 201) and the National
Defense Authorization Act for Fiscal
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Year 2015 (Pub. L. 113–291, 128 Stat.
3729, Section 3720(f)). These areas are
proposed for removal from regulatory
roadless classification because having
two layers of protection (statutory and
regulatory direction) that are
substantially similar but slightly
different does not make a meaningful
difference to the level of conservation
provided and can create confusion for
land managers, stakeholder groups, and
the public. Removal of the LUD II areas
from regulatory roadless classification is
an attempt to eliminate that confusion
while remaining consistent with the
congressionally established
management regime for the LUD II
areas. The statutory direction managing
in a roadless state for wildland character
within LUD II areas would remain in
effect regardless of which alternative is
selected.
Alternative 4 provides additional
available land base from which timber
harvest opportunities could occur while
maintaining roadless designations for
areas defined in the Tongass Forest Plan
as Scenic Viewsheds, T77 Watersheds,
and The Nature Conservancy/Audubon
Conservation Priority Areas. Additional
timber harvest opportunities are
provided by removing approximately
401,000 acres of roaded roadless areas
and adjacent extensions, as described in
Alternative 3, from roadless
classification. In addition, timber
harvest opportunities are provided by
managing approximately 757,000 acres
of Timber Production and Modified
Landscape LUDs, as defined in the
Tongass Forest Plan, in a roadless
management category called Timber
Priority, which allows for timber
harvest, road construction, and road
reconstruction.
Alternative 4 designates
approximately 7,000 acres as Alaska
Roadless Areas, which were statutorily
designated as LUD II areas, but not
included in the 2001 roadless inventory.
These 7,000 acres combined with the
LUD II areas included in the 2001
roadless inventory total 854,000 acres
that would be designated as roadless
with regulatory direction mirroring the
statutory direction.
The remaining 7,363,000 acres of
Alaska Roadless Areas in Alternative 4
would be managed as Roadless Priority,
which is similar to the 2001 Roadless
Rule, but less restrictive and addresses
Alaska-specific concerns for
infrastructure development to connect
and support local communities and
access to renewable energy and leasable
minerals.
Alternative 5 maximizes the land base
from which timber harvest
opportunities could occur by removing
2.32 million acres from roadless area
designation. Taken together, the six
alternatives represent the spectrum of
management regimes identified to the
Forest Service through public
comments, public meetings, tribal and
Alaska Native corporation
consultations, and cooperating agency
input.
The table below displays the acreage
changes from the 2001 Roadless Rule to
acreages that would be designated under
each of the six alternatives displayed in
the FEIS.
Alternatives
1
Total Roadless Acres ...............................
Roadless Acres Removed .......................
Roadless Acres Added ............................
Net Acre Change ** ..................................
2
9,368,000
0
0
0
3*
9,336,000
142,000
110,000
¥32,000
8,224,000
1,252,000
107,000
¥1,144,000
4
5
8,975,000
401,000
7,000
¥394,000
7,047,000
2,321,000
0
¥2,321,000
6 Final rule
0
9,368,000
0
¥9,368,000
* Alternative 3 has less total areas designated as roadless than Alternative 4 due to 854,000 of LUD II areas removed but they are still managed for wildland character based on statutory direction, hence Alternative 3 is more restrictive than Alternative 4.
** Numbers may not appear to sum correctly due to rounding.
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Environmentally Preferable Alternative
The environmentally preferable
alternative is the alternative that best
promotes the national environmental
policy as provided by Section 101 of the
National Environmental Policy Act
(NEPA), 42 U.S.C. 4331. In application,
the environmentally preferable
alternative causes the least damage to
the biological and physical
environment. It also best protects,
preserves, and enhances historic,
cultural, and natural resources. It is the
alternative that achieves the widest
range of beneficial uses of the
environment without degradation, risk
to health and safety, or other
undesirable or unintended
consequences.
Alternative 2 is the environmentally
preferable alternative. While it
represents a slight decrease
(approximately 32,000 acres) in total
acres to be managed as Alaska roadless
areas, all the acres designated as Alaska
Roadless Areas in Alternative 2 are
undeveloped at this time. Alternative 1
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(the 2001 Roadless Rule) includes more
total roadless acres; however,
approximately 142,000 acres have been
roaded, harvested, or significantly
altered and those lands no longer retain
the roadless characteristics and values
the 2001 Roadless Rule is intended to
conserve. In addition, approximately
110,000 acres of undeveloped land not
included in the 2001 Roadless Rule
were designated as Alaska Roadless
Areas. Alternative 2 limits timber
harvesting, road construction, and road
reconstruction on the most undeveloped
roadless acres of all the alternatives
considered. While the Roadless Priority
management category assigned to
approximately 5.2 million acres in
Alternative 2 includes more exceptions
than Alternative 1, the Watershed
Priority management category, which is
more restrictive than the 2001 Roadless
Rule, is applied to approximately 3.3
million acres in Alternative 2. For all
these reasons, Alternative 2 is the
alternative that best protects, preserves,
and enhances roadless characteristics
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and values on the Tongass National
Forest.
Decision Rationale and Important
Considerations
On July 12, 2001, the 2001 Roadless
Rule was promulgated. Views on
applying roadless restrictions on the
Tongass National Forest changed
dramatically over the course of that
rulemaking, and since. Originally, the
USDA’s proposed rule sought to exclude
the Tongass from any roadless
restrictions while promising to revisit
the question in five years. Seven months
later, the USDA’s Final EIS (FEIS)
instead identified a preferred alternative
to apply the roadless prohibitions after
a five-year delay. A mere month later,
the final Record of Decision (ROD)
instead elected to apply the regulation’s
roadless prohibitions immediately upon
the effective date of the rule.
In 2003, USDA settled litigation with
the State of Alaska challenging the
promulgation of the 2001 Roadless Rule.
The USDA proposed and finalized a
rule temporarily exempting the Tongass
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National Forest from operation of the
2001 Roadless Rule (e.g., Tongass
Exemption Rule—68 FR 75136).
However, the Tongass Exemption Rule
itself was judicially set aside in 2011,
and the 2001 Roadless Rule was
reinstated under the terms set forth in
the final judgment of the U.S. District
Court for the District of Alaska. Since
that time, no further regulatory action
regarding this matter has taken place,
and the 2001 Roadless Rule remains in
effect as to the Tongass National Forest.
Considerable congressional interest
has resulted in the introduction of
competing legislative bills designed to
alternatively codify or strike down the
operation of the 2001 Roadless Rule, in
whole or in part, since the rule was
promulgated. These legislative
proposals have included attempts to
legislate an outcome for the rule’s
application to the Tongass National
Forest, but none of these bills have been
enacted into law.
Combined with the complex, and
sometimes even conflicting, judicial
rulings applicable to the 2001 Roadless
Rule itself, the recent history of roadless
management on the Tongass National
Forest demonstrates that while
differences in opinion seem inevitable,
a wide variety of approaches are
available for roadless area management.
Roadless area management, like all
multiple-use land management, is
fundamentally an exercise in discretion
and policy judgment concerning the
best use of the NFS lands and resources,
informed by the underlying facts and
reasonable projections of possible
social, economic, and environmental
consequences.
While the Tongass National Forest has
endured debate regarding land and
natural resource management for
decades, there are common agreements.
Tongass National Forest roadless areas
are vast and valuable. The Tongass
National Forest contributes ecological
values locally, regionally, nationally,
and internationally. Local communities
are reliant on or impacted by federal
land management decisions, and there
is not always consensus, at the local
level, on land management priorities.
All acknowledge that there are diverse
opinions and views concerning whether
and how road construction and timber
harvesting should be restricted. To be
sure, the USDA has received many
comments that highlight differences in
views concerning factual matters and
methodologies, as well as general
opinions and preferences. The USDA is
grateful for the attention and interest
that communities, stakeholder groups,
and individuals have devoted to helping
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shape and improve the FEIS for
decision-making purposes.
Importantly, the final rule’s change in
policy does not fundamentally rest on
new factual findings contradicting the
factual findings the USDA made in its
2001 Roadless Rule. Rather, the policy
judgments implemented through this
new rulemaking are ultimately the
result of assigning different value or
weight to the various multiple uses.
Although many circumstances have
changed since 2001, such as the size
and economic role of the timber
industry in southeast Alaska, the nature
and role of southeast Alaska’s roadless
areas have not changed. The currentlydesignated roadless areas continue to
provide large tracts of undeveloped land
for roadless values, watershed
protection, and ecosystem health even
while the Tongass National Forest was
exempted from the 2001 Roadless Rule
from 2001 to 2011.
The FEIS carefully analyzes the
environmental consequences of both
continued operation of and exemption
from the 2001 Roadless Rule. That
analysis reveals only a modest
difference in potential environmental
consequences between those (or any)
alternatives. For example, although 9.4
million acres would no longer be subject
to the 2001 Roadless Rule with the final
rule, only 186,000 more acres would
become available for timber production,
and road construction is estimated to
increase Tongass-wide from 994 miles
in the no-action alternative to 1,043
miles in the final rule over the next 100
years. As many commenters have
pointed out, the results of this analysis
are attributable to the fact the 2001
Roadless Rule is not the primary
limiting factor for Tongass National
Forest timber harvest, and that the level
of timber harvest defined in the Forest
Plan has a greater influence. Similarly,
the 2001 Roadless Rule would not seem
to be the impediment to certain vital
infrastructure and energy projects as
claimed by some, given that some
infrastructure and energy development
is allowed under various statutes and/or
the 2001 Roadless Rule.
Under the current Administration, the
USDA has refocused policies, programs,
and resources on increasing rural
economic opportunity, decreasing
federal regulation, and streamlining
federal government services. The USDA
concludes in light of the FEIS that a
policy change for the Tongass National
Forest can be made without major
adverse impacts to the recreation,
tourism, and fishing industries, while
providing benefits to the timber and
mining industries, increasing
opportunities for community
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infrastructure, and eliminating
unnecessary regulations.
The Secretary of Agriculture has
broad authority to protect and
administer the NFS through regulation
as provided by the Organic
Administration Act of 1897 (Organic
Act), the Multiple-Use Sustained Yield
Act of 1960, and the National Forest
Management Act of 1976 (NFMA).
These statutes provide the Secretary of
Agriculture with discretion to determine
the proper uses within any area,
including the appropriate resource
emphasis and mix of uses. In doing so,
USDA considers the relative values of
the various resources and seeks to
provide for the harmonious and
coordinated management of all
resources in the combination that will
best meet the needs of the American
people. Roadless areas provide real and
important values, such as high quality
or undisturbed soil, water and air;
sources of public drinking water;
diversity of plant and animal
communities; habitat for threatened,
endangered, proposed, candidate, and
sensitive species; primitive and semiprimitive classes of dispersed
recreation; reference landscapes; natural
appearing landscapes with high scenic
quality; traditional cultural properties
and sacred sites; and other locally
identified unique characteristics.
However, roadless values are not the
only values that should be taken into
consideration. The Organic Act and
Multiple-Use Sustained Yield Act
mandate the Forest Service to manage
NFS lands for multiple uses and
sustained yield of the various renewable
surface resources to meet the needs of
the American people.
The State of Alaska’s Citizens
Advisory Committee devoted
considerable time and effort capturing
the many and varied aspects of roadless
characteristics from an Alaska-specific
viewpoint, and the USDA is grateful for
their dedication and insights. Similarly,
tribal government cooperating agencies
expressed concern about removal of the
2001 Roadless Rule but expressed an
interest in expanded regulatory
flexibility within their traditional
territories. Here too, the USDA is
grateful for their participation as
cooperating agencies and for the
knowledge and insights they have
brought to the rulemaking.
Unquestionably, there are differences
of perspective and opinion as to how to
best shape restrictions that protect a
beloved resource while providing
cultural, social, and economic benefit
for both local communities and the
nation, which is reflected in the 267,000
comments received on the proposed
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rule and DEIS (summarized in
Appendix H of the FEIS). The USDA’s
assessment is that the best mechanism
to account for these many and
competing interests is to return the
regulatory landscape back to what it was
prior to the promulgation of 2001
Roadless Rule and to allow land
management to be governed through the
NFMA forest planning process.
Alaska-Specific Statutes
The USDA has also considered
several Alaska-specific statutes
applicable to the Tongass National
Forest in selecting the final rule. To be
clear, all the alternatives considered are
within the lawful discretion of the
USDA to select, and all would comply
with applicable statutes. No statute
compels or prohibits establishment of
any of the various roadless rule
alternatives; these alternatives would all
be within the USDA’s discretion.
In assessing roadless management for
these lands, the USDA has considered
the Alaska-specific legislation that
Congress has enacted during the past
forty years, especially the TTRA and
ANILCA.
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Tongass Timber Reform Act
The TTRA directs the Forest Service
to seek to provide a supply of timber
from the Tongass National Forest that
meets annual market demand and the
market demand for each planning cycle
to the extent consistent with providing
for the multiple-use and sustained-yield
of all renewable resources and other
applicable requirements, including the
NFMA. The Tongass Forest Plan
anticipates sufficient timber availability
to meet projected demand as described
in the 2016 Forest Plan FEIS and ROD.
In addition, the Tongass Forest Plan
provides guidance to conduct annual
monitoring and review of current timber
demand. Similarly, TTRA provides for
protection of riparian habitats and the
multiple use and sustained yield of all
renewable surface resources.
Alaska National Interest Lands
Conservation Act—Subsistence
Determination
ANILCA, as amended, contains
several provisions that apply to
management of the Tongass National
Forest. An ANILCA Section 810
evaluation and determination is not
required to exempt the Tongass National
Forest from the 2001 Roadless Rule—a
rulemaking process and programmaticlevel decision that is not a
determination whether to ‘‘withdraw,
reserve, lease, or otherwise permit the
use, occupancy, or disposition’’ of NFS
lands. However, a forest-wide
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evaluation and determination is
included in this roadless area
rulemaking to honor regional
commitments and inform future projectlevel planning and decision-making
subject to ANILCA Section 810 (16
U.S.C. 3120). An ANILCA Section 810
subsistence analysis and determination
was not prepared when the 2001
Roadless Rule was promulgated.
The final rule has been evaluated for
potential effects on subsistence uses and
needs in a manner consistent with
Section 810 of ANILCA. The FEIS
discloses direct, indirect, and
cumulative effects on three subsistence
use factors including: (1) Resource
distribution and abundance; (2) access
to resources; and (3) competition for the
use of resources (Chapter 3,
Subsistence). Importantly, the final rule
does not authorize ground-disturbing
activities, but instead offers greater
flexibility in locating future road
construction, road reconstruction, and
timber harvest activities. The Tongass
Forest Plan will continue to guide
timber harvest and road construction,
with the administrative change
prescribed in this rule only serving to
conform and clarify the lands available
for timber harvest following the
exemption from the 2001 Roadless Rule.
Consequently, total timber harvest
volume will remain constant across
alternatives, and the risk of a significant
restriction to subsistence resource
abundance and distribution is largely
equivalent across alternatives. The final
rule may eventually influence
subsistence resource access due to
timber management activities, but these
changes will be addressed on a sitespecific basis, including appropriate
public engagement opportunities, as
projects are proposed.
Competition for subsistence wildlife
and seafood resources near rural
communities is affected by a variety of
factors including regulations,
technology, wildlife distribution, modes
of access, and natural decreases in
population. The final rule assumes new
roads near communities connected to
other communities by ferry or road,
combined with increasing habitat
reductions and consistent user demand,
will likely increase subsistence resource
competition over time.
Based on the identified assumptions
and analysis, the final rule may
eventually indirectly result in a
significant restriction of subsistence use
of deer by increasing overall
competition for the subsistence resource
by urban and rural residents. This
finding is most applicable to Chichagof,
Baranof, and Prince of Wales Islands
where competition for deer and some
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other land mammals is already high and
habitat capacity has been significantly
reduced due to prior timber harvest and
road construction activities. Notably,
the predicted restriction of subsistence
use of deer due to increased competition
in the FEIS is substantially similar to
Forest Plan subsistence effects analysis
because the Forest Plan will continue to
guide total timber harvest volume.
ANILCA subsistence hearings were
conducted for the DEIS and proposed
rule, consistent with Section 810, by: (1)
Giving notice to the appropriate state
agency, local committees, and regional
councils; and (2) giving notice of, and
holding, ‘‘a hearing in the vicinity of the
area involved.’’ As the geographic area
of interest is the entire Tongass National
Forest, subsistence hearings were
conducted in 18 communities located
across southeast Alaska to collect oral
testimony regarding the DEIS and
associated subsistence resource and use
analysis.
Section 810 requires that when a use,
occupancy, or disposition of public
lands may result in a significant
subsistence use restriction, a
determination must be made whether:
(A) Such a significant restriction of
subsistence uses is necessary, consistent
with sound management principles for
the utilization of the public lands, (B)
the proposed activity will involve the
minimal amount of public lands
necessary to accomplish the purposes of
such use, occupancy, or other
disposition, and (C) reasonable steps
will be taken to minimize adverse
impacts upon subsistence uses and
resources resulting from such actions.
Each of these three points are discussed
below.
Necessary, Consistent with Sound
Management of Public Lands. The final
rule has been examined to determine
whether the potential for a significant
restriction of subsistence uses is
necessary, consistent with the sound
management of NFS lands. The final
rule is designed to provide a mix of
resources and benefits to best meet the
needs of the American people. Some of
the resource uses necessary to achieve
these benefits have the potential to
adversely affect subsistence uses within
the Tongass National Forest. In light of
the Forest Service’s multiple-use
mandate and other requirements of law,
the Forest Service has determined that
these effects to subsistence uses are
necessary and consistent with the sound
management of NFS lands. (The Forest
Service again notes that making this
determination is not required for
purposes of issuing this rule, but it is
the Department’s policy preference to
make this determination, and the other
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determinations explained below related
to ANILCA Section 810, on a voluntary
basis in light of the considerations noted
above.)
Amount of Public Land Necessary to
Accomplish the Purposes of the
Proposed Action. The land area
evaluated through this rulemaking is the
Tongass National Forest and the IRAs
therein. These lands constitute the
amount of land necessary to assess
operation of the 2001 Roadless Rule
within the Tongass National Forest as
requested by the State of Alaska’s
petition. This rulemaking considered
applying various prohibitions and
exceptions to different numbers of acres
through the development and analysis
of a range of alternatives. The final rule,
however, removes the 2001 Roadless
Rule’s land classification system and
associated prohibitions and exceptions,
and allows management to return to
operation under the Forest Plan.
Accordingly, the final rule addresses the
amount of NFS land necessary to
accomplish the proposed action.
Reasonable Steps to Minimize
Adverse Impacts to Subsistence Uses
and Resources. The continuation of
subsistence opportunities, and
reasonable steps to minimize effects on
subsistence resources, are provided by
Tongass Forest Plan forest-wide
standards and guidelines for
subsistence, as well as related standards
and guidelines for riparian areas, fish,
and wildlife. Many important
subsistence areas are assigned LUDs that
exclude timber harvesting and road
construction. Beach and estuary fringe
forest-wide standards and guidelines
generally apply to beach fringe and
estuarine areas not under more
restrictive designations. Adverse
impacts to subsistence resources and
uses are minimized through these
measures. The potential site-specific
effects on subsistence uses, and
reasonable ways to minimize these
effects, will be analyzed and considered
during project-level design and
decision-making.
The final rule does not authorize
ground-disturbing activities, but instead
offers greater flexibility in locating
future development activities on the
Tongass National Forest. It is not
possible to substantially reduce timber
harvest in some areas by concentrating
it in other areas without affecting
subsistence resources and uses
important to other communities. Also,
concentrating timber harvest outside
more important subsistence areas while
still meeting Tongass Forest Plan timber
harvest goals could not be done without
affecting the natural distribution of
wildlife species or without potential
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significant effects to watersheds. These
potential environmental effects will be
comprehensively studied and disclosed
through the future analysis of Tongass
National Forest projects.
2001 Roadless Rule’s Original Purpose
The USDA is mindful of the original
stated purposes of the 2001 Roadless
Rule in lifting the rule’s restrictions for
the Tongass National Forest. The stated
purposes of the 2001 Roadless Rule
included retention of the largest and
most extensive tracts of undeveloped
land for the roadless values, watershed
protection, and ecosystem health; and
fiscal considerations, mainly the cost of
managing the road system to safety and
environmental standards. Specific to the
Tongass, the 2001 Roadless Rule’s
Record of Decision noted that social and
economic considerations were key
factors in analyzing alternatives, along
with the unique and sensitive ecological
character of the Tongass National
Forest, the abundance of roadless areas
where road construction and
reconstruction are limited, and the high
degree of ecological health. (66 FR
3254). The past 20 years of experience
managing the Tongass National Forest,
with and without the rule in operation,
provides an important window for
assessing whether the 2001 Roadless
Rule’s prohibitions should be
maintained.
From 2001 to 2011, the Tongass
National Forest was exempt from the
2001 Roadless Rule. During this time,
about 4,300 acres of IRAs were entered
for timber harvest and about 19 miles of
roads were constructed in association of
that timber harvest. Of that only 300
acres of timber harvest and 0.5 miles of
road were authorized during the
exemption period and the remaining
timber harvest and road construction
were authorized prior to the
promulgation of the 2001 Roadless Rule.
After the harvest units and roads are
buffered in GIS, this accounts for about
one percent of the substantially altered
areas (roaded roadless areas) removed
from roadless designation in
Alternatives 2 through 5. The remaining
99 percent of the roaded roadless areas
are from mapping errors and activities
that occurred before 2001 (36%) or were
allowed under the 2001 Roadless Rule
(62%).
A significant percentage of the
Tongass National Forest remains
undeveloped, providing for large,
extensive tracts of undeveloped land,
but much of that is characterized as
rock, ice, or muskeg. The final rule will
make an additional 188,000 forested
acres available for timber harvest with
the majority characterized as old-growth
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timber. The young-growth transition
strategy as described in the 2016
Tongass Forest Plan ROD outlines a
glide path to decrease old-growth
harvest annually on the Tongass until it
reaches about 5 million board feet
(MMBF) harvest per year, expected to
occur in about 2032. After the younggrowth transition is fully implemented,
it is unlikely that a significant portion
of the areas previously designated as
IRAs would be considered for harvest
because the focus for timber harvesting
will shift to the previously roaded,
young-growth areas.
Watershed protection was a
prominent aspect in the decision to
adopt the nationwide 2001 Roadless
Rule. Looking at the Tongass National
Forest today, watershed protection goals
are well provided for even without the
current roadless rule. Large tracts of
undeveloped lands and watershed
protections are provided by existing
statutory and forest plan direction,
including lands in designated
Wildernesses and National Monuments.
In addition, the TTRA (Pub. L. 101–626,
Title II, Section 201) and the National
Defense Authorization Act for Fiscal
Year 2015 (Pub. L. 113–291, 128 Stat.
3729, Section 3720(f)) designated
approximately 856,000 acres as LUD II
areas, which are managed in a roadless
state to retain their wildland character.
Approximately 3.6 million acres in key
watersheds (defined in the Forest Plan
as Tongass 77 Watersheds and The
Nature Conservancy/Audubon
Conservation Areas) are managed for no
old-growth timber harvest, thus
minimizing adverse impacts to fisheries.
Management direction of LUD II areas
and key watersheds would remain
unaffected with the final rule.
Ecosystem health was another
important element of the 2001
rulemaking. Once again, the FEIS
reveals only a moderate difference
between implementation of the 2001
Roadless Rule and the final rule. A key
indicator of ecosystem health for the
Tongass National Forest is a functional
and interconnected old-growth
ecosystem. Under the final rule, longterm protection of productive old
growth would continue to occur under
the Forest Plan’s old-growth habitat
conservation strategy. Connectivity
between old-growth reserves would
continue to be maintained through
Forest Plan direction for stream buffers,
the beach and estuary fringe, and legacy
forest structure. Under the final rule, the
projected amount of old-growth harvest
and percent of original productive oldgrowth remaining over the next 100
years would remain unchanged from
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implementation of the 2001 Roadless
Rule (Alternative 1—No Action).
Although it may seem counterintuitive that eliminating the 2001
Roadless Rule’s timber harvest
restrictions across 9.3 million acres
would not increase old-growth timber
harvest, timber harvest levels are
controlled to a far greater extent by
other factors, primarily economic
factors. Additionally, the Forest Plan’s
young-growth transition strategy will
transition harvest locations away from
roadless areas containing old growth
and into areas where timber harvest has
previously occurred, avoiding or
reducing effects to roadless areas. The
underlying economic considerations
and the young-growth transition strategy
are far greater influences than the 2001
Roadless Rule. This strategy will remain
in place, with or without the 2001
Roadless Rule.
Limited road maintenance budgets
were another factor cited in support of
the 2001 Roadless Rule. The 2001
Roadless Rule cited fiscal concerns over
building new roads in IRAs due to an
$8.4 billion backlog of deferred
maintenance across the NFS
transportation system at that time.
Recent deferred maintenance records
were reviewed; a sound comparison
could not be made with the deferred
maintenance levels of 2001, due to
substantial changes in defining and
interpreting deferred maintenance.
Since 2001, the inventory methods and
roads considered to be part of deferred
maintenance have changed multiple
times (2002, 2005, 2007, 2012, and
2013). These changes make a direct
comparison with 2001 deferred
maintenance numbers impracticable.
The FEIS projects that about 1,043
miles of new road construction could
occur over the next 100 years across the
Tongass National Forest, mainly to
support timber harvest operations, as
compared with the approximately 994
miles of new roads projected forest-wide
over the next 100 years under
Alternative 1—No Action. The 994
miles of new road construction
projected for Alternative 1 are outside of
inventoried roadless areas. The final
rule is not expected to materially
increase the amount of timber harvested
in the Tongass, as that is prescribed and
managed by the Forest Plan. However,
the final rule does impact the location
from which the timber may be
harvested, by allowing access to areas
that were off limits under the 2001
Roadless Rule.
National Versus Local Decision-Making
For decades, the USDA has worked
with states, tribes, local communities
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and collaborative groups toward land
management solutions for roadless
areas. Sometimes solutions have been
found nationally. Sometimes a state-bystate approach has been the best option.
Often, the solutions are found forest-byforest or even area-by-area. In this
instance, the national rule’s one-sizefits-all approach to roadless area
management is not the best approach for
roadless area management on the
Tongass National Forest. Other states,
Idaho and Colorado, have sought and
been granted the opportunity for
roadless management to be tailored to
their needs. Indeed, the USDA received
at least thirteen individual state
petitions seeking various state-specific
solutions during the timeframe in which
the 2001 Rule had been judicially
invalidated. The State of Alaska’s 2018
rulemaking petition implores the USDA
to recognize that in contrast to the
scarcity of undeveloped lands that
occurs in many other states,
undeveloped areas are plentiful in
Alaska. Instead, the State of Alaska
maintains that the circumstances of the
Tongass National Forest appear to be
best managed through the local
planning processes. The Forest Service’s
40 years of experience with forest
planning under NFMA, which includes
forest plans subject to periodic review
and adjustment, routinely demonstrates
the planning system’s capacity to
account for both local and national
interests and provide durable and
widely accepted solutions providing for
the multiple use and sustained yield of
the many goods and services provided
by the NFS.
The final rule would leave the
roadless area management issue open
for future consideration in the forest
planning process. The forest planning
process is more flexible than the 2001
Roadless Rule’s regulatory approach,
because plans are expected to be
designed and attuned to local
circumstances and are intended to be
periodically reviewed. The 2001 Rule’s
prescriptive approach forecloses a full
balancing of interests during future
forest planning processes. The final rule
will allow local decision makers the
flexibility to address roadless
management based on changed local
conditions, new unforeseen issues, and
take into account state and local
economic development plans. In
addition, the final rule will provide
local discretion during future forest
planning efforts to explore roadless area
management alternatives, unconstrained
by the 2001 Roadless Rule, with local
stakeholders, communities, and tribal
governments.
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In selecting the final rule among the
several alternatives considered, the
USDA has given substantial weight to
the State of Alaska’s policy preferences
as expressed in its Petition. The State of
Alaska’s preference to emphasize rural
economic development opportunities is
consistent with the findings of the
Interagency Task Force on Agriculture
and Rural Prosperity established by
Executive Order 13790 issued April 25,
2017.1 The USDA recognizes that
ensuring rural Americans can achieve a
high quality of life is one of the
foundations of prosperity.2 The State of
Alaska’s views on how to balance
economic development and
environmental protection offer valuable
insight when making management
decisions concerning NFS lands within
Alaska.
Southeast Alaska’s rural communities
have relied upon the Tongass for
important natural resources and
environmental opportunities supporting
recreation, fishing, and the timber
industries. In particular, the timber
industry has historically played an
important economic role in southeast
Alaska’s rural economy providing jobs
in small and remote communities with
high unemployment rates and limited
employment opportunities. In these
isolated communities, every job has
impacts at household and community
levels. Notably, the timber industry has
faced sustained hardship during the
past two decades, with rural
communities suffering the
socioeconomic consequences. The final
rule will increase the number of acres
available for timber harvest acres and
improve overall flexibility in locating
timber sales. In turn, this would provide
additional opportunity for the struggling
timber industry and support rural
communities with limited employment
opportunities without increasing the
amount of overall timber harvested.
USDA and the State of Alaska believe
both roadless area conservation and
other multiple-use values with
important local socioeconomic
consequences are meaningfully
addressed through local and regional
forest planning on the Tongass National
Forest without 2001 Roadless Rule
prohibitions on timber harvest and road
construction/reconstruction.
The USDA recognizes that the
majority of Alaska Native tribes and
1 See Report to the President of the United States
from the Task Force on Agriculture and Rural
Prosperity (Oct. 21, 2017), https://www.usda.gov/
sites/default/files/documents/rural-prosperityreport.pdf).
2 See id. at 2, 21–25; see also id. at 26–29, 35–
42 (calls to action for supporting a rural workforce
and developing the rural economy).
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local communities throughout southeast
Alaska support keeping the 2001
Roadless Rule in place, as expressed in
the multitude of resolutions and
comment letters received during the 60day comment period. USDA appreciates
that not all local communities share the
State of Alaska’s views and has carefully
considered the views and preferences
provided by all the leaders and citizens
that have participated through various
public meetings and comment periods.
The USDA urges those groups and
individuals to regularly engage with the
Tongass National Forest and Forest
Service Alaska Region concerning forest
planning efforts and project design. The
lifting of the 2001 Roadless Rule on the
Tongass National Forest in no way
impedes citizen participation; rather, it
affords interested parties the
opportunity to work with the Forest
Service to seek more efficient solutions
that account for all interests.
Relationship of the Alaska Roadless
Rule to the Forest Plan
The NFMA requires the Forest Service
to develop, maintain and, as
appropriate, revise land and resource
management plans for units of the NFS.
Land management plans provide a
framework for integrated resource
management and for guiding project and
activity decision-making, but plans do
not authorize projects or activities or
commit the Forest Service to take
action. A revised Tongass Forest Plan
was issued in 1997 and amended in
2008 and 2016. Forest planning is a
distinct and separate process from
USDA’s various roadless rulemakings.3
Excluding the Tongass from the 2001
Roadless Rule’s prohibitions returns
management discretion to the Agency’s
standard planning process. The existing
Forest Plan provides adequate direction
and protection of roadless
characteristics such that retention of the
2001 Roadless Rule is not required.
Future plan revisions will assure
roadless characteristics are periodically
assessed and management direction can
be adjusted if warranted (increased,
decreased or blended differently) in
order to account for the best multiple
use management possible.
All forest plans must conform to
existing laws and regulations as well as
new laws and regulations. See 36 CFR
219.1(f) and 219.13(c). The USDA’s
previous roadless rules, national and
state-specific, have directed that: (1) No
amendment or revision of any forest
3 See Kootenai Tribe of Idaho v. Veneman, 313 F.
3d 1094, 1117 n.20 (9th Cir. 2002), abrogated on
other grounds by Wilderness Society v. USFS, 630
F.3d 1173 (9th Cir. 2011); and Wyoming v. USDA,
661 F.3d 1209, 1269–72 (10th Cir. 2011).
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plan was compelled by promulgation of
such rules; (2) subsequent forest
planning decisions could not revise the
Secretary’s regulatory instructions; and
(3) line officers were to conform project
decisions to the prohibitions and
exceptions set forth in the applicable
rules. The final rule continues this
approach, with one exception
necessitated by a single element of the
2016 Tongass Forest Plan Amendment.
The final rule directs the Tongass
Forest Supervisor to issue a ministerial
Notice of Administrative Change
pursuant to 36 CFR 219.13(c)
identifying plan changes made in
conformance with the regulatory
determinations of this subpart;
specifically the rescission of the portion
of the December 9, 2016, ROD
concerning suitable timber lands
attributed exclusively to
implementation of the January 12, 2001,
Roadless Area Conservation Rule (66 FR
3244). This administrative change is
appropriate because the Region took the
step in 2016 of amending the Tongass
Forest Plan to directly implement the
2001 Roadless Rule’s timber harvesting
prohibitions despite the 2001 Roadless
Rule’s express admonition that it did
not compel the amendment or revision
of any land and resource management
plan. See 2016 Tongass Forest Plan,
Appendix A, page A–3, Appendix I,
page I–177 (indicating all IRA were
removed from the suitable land base
during Stage 1 of the suitability analysis
due to the 2001 Roadless Rule) and 36
CFR 294.14(b) (directing that the 2001
Rule does not compel the amendment or
revision of any land and resource
management plan). The 2016 Forest
Plan sought to directly implement the
2001 Roadless Rule prohibitions via the
timber suitability analysis. Today’s
decision to rescind the 2001 rule’s
prohibition as to the Tongass National
Forest makes the 2016 Amendment’s
effort to implement the 2001 rule’s
prohibitions obsolete. Because allowing
the inconsistent portion of the 2016
suitability designations to stand would
effectively nullify the Department’s
regulatory choice to remove the 2001
timber harvest prohibitions, the final
regulation gives an express regulatory
instruction to conform the plan to the
new regulatory regime. As explained in
greater detail below, there is no
requirement or credible justification that
warrants undertaking additional
planning efforts above and beyond the
administrative change directed by this
rulemaking. The administrative change
simply provides conformance of the
Forest Plan with the final rule in regard
to lands suitable for timber production
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and does not change the level of timber
harvest, how timber is harvested on the
Tongass, or any other aspects of the
Forest Plan.
As previously noted, forest planning
is a distinct and separate process from
USDA’s various roadless rulemakings.
The referenced 2001 Roadless Rule’s
scope and applicability language was
designed to avoid conflicts between
itself and forest plans, as well as
avoiding unnecessary or duplicative
administrative processes for the
operation of the 2001 Roadless Rule.
Just as it was unnecessary to
immediately install the 2001 Roadless
Rule’s higher order prohibitions through
individual plan amendments, it is
unnecessary here to duplicate these
rulemaking efforts through a separate
plan amendment. Fortunately, the 2012
NFMA planning regulations (36 CFR
219.13(c)) make provision for instances
where overriding statutes or regulations
change. The planning regulations direct
that plans may be adjusted via notice of
administrative change without resorting
to the standard plan amendment
process. The USDA is empowered to
prescribe such regulations as it
determines necessary and desirable to
carry out the planning process (16
U.S.C. 1613) as well as to redeem and
reconcile its regulations governing
overall multiple use management
responsibilities, including roadless
matters.
To promote clarity, transition
language has been added to the final
rule. The language is similar as was set
out for the other action alternatives in
the DEIS. The operational result will be
that 188,000 acres will be returned to
the suitable timber base via the
administrative change provision of the
planning regulations (36 CFR 219.13(c)).
The revised transition language assures
that all other aspects of the Tongass
Forest Plan remain operational under
the rule including the goals, objectives,
management prescriptions, standards,
guidelines, projected timber sale
quantity, projected wood sale quantity,
and the young-growth transition
strategy. This includes direction for
non-timber resources including riparian
management standards and guidelines,
which provide protection for fisheries
with subsistence and commercial
importance. Any timber harvest,
including any timber harvesting in areas
formerly designated as IRAs, would be
compelled to adhere to these resource
standards and guidelines including fish
habitat, water quality, air, recreation,
and other resources. Consistency with
Forest Plan direction continues under
all alternatives.
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Although the Forest Service has broad
discretion to amend or revise forest
plans management direction, any
change would need to be consistent
with applicable law, regulation, and
policies. Any future forest plan
amendments or revisions would include
a public involvement process pursuant
to the Agency’s planning regulations
and NEPA.
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Public Comment Process
The Forest Service published an NOI
to prepare an EIS for the Alaska
Roadless Rule in the Federal Register
(83 FR 44252) on August 30, 2018. The
NOI initiated a 45-day scoping period
which ended on October 15, 2018.
During this time period, the Forest
Service conducted 17 public meetings
including meetings in Anchorage, AK;
Washington, DC; and communities
throughout southeast AK: Angoon,
Craig, Gustavus, Hoonah, Kake,
Ketchikan, Petersburg, Point Baker,
Sitka, Tenakee Springs, Thorne Bay,
Wrangell, Yakutat, and two meetings in
Juneau. During the scoping period, just
over 144,000 comment letters or emails
were received.
On October 17, 2019, the Department
published a notice of proposed
rulemaking in the Federal Register (84
FR 55522) and on October 18, 2019, an
NOA for the DEIS was published (84 FR
55952). On October 25, 2019 an
amended NOA was published (84 FR
57417) which amended the comment
closing date of the 60-day comment
period to December 17, 2019. During the
60-day comment period, the Forest
Service conducted 21 public meetings
including Anchorage, Alaska;
Washington, DC; and southeast Alaska
communities: Angoon, Craig, Gustavus,
Haines, Hoonah, Hydaburg, Juneau,
Kake, Kasaan, Ketchikan, Pelican,
Petersburg, Point Baker, Sitka, Skagway,
Tenakee Springs, Thorne Bay, Wrangell,
and Yakutat. Approximately 267,000
comment letters or emails were received
during the 60-day comment period,
including 11 petitions containing about
117,000 signatures.
Cooperating Agencies
On July 30, 2018, the Forest Service
invited 32 Alaska federally recognized
tribes to participate as cooperating
agencies during the rulemaking process.
Originally six tribes agreed to become
cooperating agencies including Angoon
Community Association, Central
Council Tlingit and Haida Indian Tribes
of Alaska, Hoonah Indian Association,
Hydaburg Cooperative Association,
Organized Village of Kake, and
Organized Village of Kasaan. After the
publication of the proposed rule
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(October 17, 2019), the Organized
Village of Kake withdrew as a
cooperating agency. After the
publication of the FEIS (September 25,
2020), the remaining tribal cooperating
agencies, Angoon Community
Association, Central Council Tlingit and
Haida Indian Tribes of Alaska, Hoonah
Indian Association, Hydaburg
Cooperative Association, and Organized
Village of Kasaan withdrew as
cooperating agencies.
The State of Alaska agreed to become
a cooperating agency on August 2, 2018.
Cooperating agencies participated
throughout the rulemaking, providing
their knowledge and expertise to design
alternatives, analyze alternatives, and
refine the analysis set out in the DEIS
and FEIS.
The Forest Service made several trips
to several of the villages to work
individually with tribal cooperators,
provide technical expertise, and collect
input. All tribal cooperators opposed
the proposed rule (Alternative 6),
however, were supportive of additional
local control, increased opportunity for
local forest product businesses, and
limited increased access for a variety of
local needs.
Based on input from tribal
cooperating agencies, USDA considered
the use of the Alaska Native tribes’
traditional use areas for the community
use analysis boundaries in the
development of the DEIS. USDA did not
utilize the traditional use areas for the
impact analysis because they are
considerably larger than the community
use areas. The use of larger analysis
areas diffuses the impacts and the
Agency wanted the impacts to be
focused by community. The Agency
added an appendix displaying the
traditional use areas to recognize the
importance of the traditional use areas
to the Alaska Native tribes.
The Agency revisited the analysis
boundary issue between the DEIS and
FEIS, and solicited subsistence use data
by community from the State of Alaska.
Alaska Department of Fish and Game
provided updated survey information
from six communities regarding areas of
subsistence gathering. Data indicate
southeast Alaskans are traveling further
for subsistence gathering, meaning the
community use areas are larger. Again,
the larger area would diffuse the
impacts. The agency determined this
would not be an improvement to the
impact analysis and would make it more
difficult for readers to determine the
impacts.
The USDA appreciates and recognizes
the contributions of the five Alaska
Native tribes who withdrew as
cooperating agencies on October 13,
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2020. The USDA understands that the
final rule is not the outcome the tribal
cooperating agencies had hoped for, and
the Department recognizes the concerns
they expressed. The Department and
Forest Service greatly value each tribal
cooperating agency. The participation
and advice of tribal cooperating
agencies improved the analyses and
alternatives. The Department’s hope is
that removal of the 2001 Roadless Rule’s
blanket prohibitions will create space
for more creative solutions that are
sensitive to the diverse interests of
Alaskan Native Tribal communities. As
the tribal cooperating agencies’
withdrawal letter eloquently suggests,
the Department too desires to invest in
solutions that will tend the land and
serve the people.
Comments on the Proposed Rule
Approximately 267,000 comments
were received on the proposed rule and
DEIS, including 11 petitions containing
about 117,000 signatures, during the 60day comment period. A large majority of
written comments and oral subsistence
testimony supported retaining the 2001
Roadless Rule on the Tongass National
Forest. Notably, a significant proportion
of the 267,000 comments letters were
from outside Alaska. A significant
proportion of southeast Alaska
municipal and tribal governments
submitted resolutions supporting the
2001 Roadless Rule’s application on the
Tongass National Forest. However,
many of the State’s elected officials,
including the Governor, the federal
delegation, and some municipal
governments support changing the 2001
Roadless Rule. The USDA considered
all substantive comments as part of the
rulemaking, including testimony given
at the subsistence hearings. The
following is a summary of the comments
received relating the final rule and the
agency response. A full detailed
response to comments is contained in
Appendix H of the FEIS.
§ 294.50 Tongass National Forest.
No substantive comments were received
in regard to the rule language for this
section. Therefore, no changes were
made to this section.
§ 294.51 Chugach National Forest.
Comments were received expressing
concerns regarding the proposed
administrative correction and boundary
modification provisions for the Chugach
National Forest. Commenters and
cooperating agencies were concerned
that the proposed provisions were too
broad and could be used by the Forest
Service to open significant portions of
the Chugach to additional logging.
Based on the experience of
implementing the 2001 Roadless Rule,
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boundary modifications are sometimes
needed to account for errors, better
mapping technology, land exchanges,
etc. Thus, the two state-specific roadless
rules, Idaho and Colorado, have
administrative correction and
modification provisions (36 CFR 294.27
for Idaho and 36 CFR 294.47 for
Colorado) that operate differently than
the 2001 Roadless Rule. The intent of
the administrative correction and
modification provisions for Alternatives
2 through 5 was to align processes and
install a single system for the two
National Forests of Alaska. However,
some members of the public expressed
alarm that the provision could be used
to entirely undo roadless protections on
the Chugach National Forest. This was
never USDA’s intent. While alignment
of administrative procedures between
all state-specific roadless rules might
have offered some administrative
efficiencies for managing roadless
boundaries nation-wide, the final rule
gains some administrative efficiencies
by fully removing roadless rule
provisions for the Tongass National
Forest.
Section 294.51 has since been retitled
as ‘‘Transition,’’ and now includes the
instruction to the Tongass Forest
supervisor to issue an administrative
change in regard to the lands suitable
for timber production. This provision
was inadvertently not included in the
Alternative 6 rule language but was
included in Alternatives 2 through 5
rule language and noted in the DEIS as
applying to the final rule.
Comments regarding perceived
impropriety associated with the State’s
petition. Commenters expressed
concern that the State developed the
petition and the Secretary accepted the
petition without public involvement,
and that the petition was motivated by
politics and outdated timber economics.
The APA and USDA’s implementing
regulation (7 CFR 1.28) allows any
interested person to petition the
Secretary to change a regulation. There
is no prescribed process for developing
or responding to a petition other than
that it must be given prompt
consideration and the petitioner will be
notified promptly of the disposition
made of their petition. The Secretary
has no control over the underlying
motivations or data offered in support of
a petition. However, once a petition is
accepted, a rulemaking in response to a
petition will be conducted in
compliance with applicable law and
regulations. The USDA has conducted
this rulemaking in compliance with all
applicable law and carefully considered
the information provided by all those
who participated in the various public
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meetings and comment periods. The
Department has drawn its own
conclusions based on the information
provided by all parties and its own
analysis.
Comments on sufficiency of public
outreach and involvement. Commenters
raised concerns regarding whether the
length of comment periods and the
quantity and locations of public
meetings were sufficient.
The Forest Service conducted two
cycles of public comment: the first was
a 45-day scoping period from August 30,
2018, to October 15, 2018, in which
about 144,000 comment letters were
received; and the second was a 60-day
comment period on the proposed rule
and DEIS from October 18, 2019, to
December 17, 2019, which resulted in
about 267,000 comment letters. During
the scoping period 17 public meetings
were held and during the comment
period 21 public meetings were held
throughout southeast AK, Anchorage,
AK, and Washington, DC. The USDA
recognizes that many would have
desired long scoping and comment
periods. The length of the scoping and
comment periods are standard for both
the rulemaking and EIS processes. The
robust meeting attendance and the
411,000 total comments received
indicates the timing and length were
clearly adequate for many.
Comments on consideration of public
input. Commenters were concerned that
input from the public was ignored
because a large majority of comments
supported retaining the 2001 Roadless
Rule and opposed the full exemption,
which was identified as the proposed
rule and preferred alternative.
The USDA values the comments
received, and the concerns expressed
during the rulemaking process. The
USDA considered public comments
received, the range of alternatives
examined in the DEIS and FEIS, and
input from cooperating agencies and
elected officials. Public comments were
utilized to craft the range of alternatives
examined in the DEIS and FEIS, modify
the alternatives between DEIS and FEIS,
and modify analyses. The NEPA and
rulemaking public comment process are
not vote-counting processes. Every
comment has value, whether expressed
by one individual or thousands. The
public comment process considers the
substance of each individual comment
rather than the number received. No
interest group’s views or comments are
given preferential treatment or
consideration, and comments are
considered without regard to their
origin, commenter’s affiliation, or
number received. Based on the
comments received, the Secretary
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reconsidered all alternatives and has
opted for alternative 6, the full
exemption alternative.
Comments on tribal government-togovernment consultation. Commenters
expressed concern that tribal
consultation was inadequate.
In 2018, the Forest Service sent letters
to the 32 federally recognized tribes and
27 Alaska Native corporations in
southeast and southcentral Alaska to
invite government-to-government and
government-to-corporation consultation.
The in-region consultation invitation
was continuous throughout the
rulemaking process.
The Alaska Region and the Tongass
National Forest have an ongoing
government-to-government relationship
with all federally recognized tribes in
southeast Alaska. The agency will
continue to meet its responsibility to
consult with federally recognized tribes
and Alaska Native corporations through
government-to-government and
government-to-corporation consultation
on all topics. In addition to district
rangers, Regional Office staff also met
with tribes, tribal cooperators, and other
interested parties to answer questions
and provide information as requested
when feasible. Forest and Regional
Office staff provided briefings,
information meetings, supported formal
consultations, and formal public
hearings in or within the vicinity of
communities throughout southeast
Alaska. Most tribal governments took
advantage of these opportunities. To
date, twelve government-to-government
consultations have occurred in
association with this rulemaking effort.
Comments on the State’s Citizen
Advisory Committee. Commenters
expressed concerns regarding the
composition and role of the committee
in the rulemaking process, whether the
committee had undue influence, and
whether their involvement violated the
Federal Advisory Committee Act
(FACA).
The committee was established by the
State of Alaska under an Administrative
Order issued by Governor Walker in
September 2018. The committee was
charged with providing
recommendations to assist the State of
Alaska in fulfilling its role as a
cooperating agency. The thirteen
committee members were selected by
Governor Walker, and the USDA and
Forest Service had no part in the
selection. The Forest Service provided
an individual to participate on the
committee as a non-voting member to
provide procedural and technical
information to the committee.
The committee does not meet the
definition of an advisory committee as
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defined by the FACA implementing
regulations at 41 CFR 102–3.25. The
committee was established under state
law by the Governor of Alaska. The
committee reported directly to the
Governor who submitted the
committee’s report to the USDA as part
of the State’s participation as a
cooperating agency. Intergovernmental
coordination with the Governor or his
appointees is not subject to FACA. In
any event, the USDA and Forest Service
did not manage or control the
committee’s operation and did not
utilize its work within the meaning of
FACA. USDA’s involvement with the
committee was limited to non-voting
participation, providing technical
assistance. The committee did not have
undue influence over the rulemaking
process.
Comments on support to the State of
Alaska. Commenters expressed concern
that granting funds to the State of
Alaska to support the State’s
involvement in the Alaska roadless
rulemaking process was a misuse of
congressional appropriations.
The agency provided the State of
Alaska’s Forestry Division with $2
million from the fiscal year 2018
Consolidated Program Grant (CPG),
Modification 2, utilizing the State Fire
Assistance budget line item as the
source code. The modification
discussed the specific use of the
funding, which could be used for:
convening and facilitating a group with
a diverse mix of state-specific interests
to inform the State’s input as a
cooperating agency, public meetings,
cooperating agency support, economic
analysis and planning, and to
coordinate the proposed state rule with
existing land management planning
efforts in progress within the State of
Alaska. A subsequent modification has
been executed utilizing $1.3 million of
the funding to undertake wildland fire
risk reduction projects in several Alaska
communities, primarily construction of
fuel breaks and maintenance of
established fuel breaks. USDA Office of
the Inspector General has been asked to
investigate this matter and the agency is
cooperating with the investigation.
Comments on the need to change
from the 2001 Roadless Rule.
Commenters highlight that the DEIS
projects minimal benefit for the forest
products industry and thus contend that
the analysis does not support the
conclusion that eliminating the roadless
rule will support rural economic
development. In addition, commenters
questioned any need for change and
rationale in the Notice of Proposed
Rulemaking to support a change.
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USDA’s approach to rural economic
development is a long-term multifaceted strategy outlined in the Report
to the President of the United States
from the Task Force on Agriculture and
Rural Prosperity (October 21, 2017),
which includes regulatory reform,
increasing the production of natural
resources, modernizing rural utilities,
and improving transportation
infrastructure. The final rule reduces the
regulatory barrier to achieving these
aspects of USDA’s strategy for rural
economic development. Although there
is only a minimal benefit from the final
rule to the forest products industry at
this time, small incremental change can
help achieve rural prosperity over the
long-term. The final rule is a step in the
right direction for rural prosperity.
Comments on a local approach for
roadless management. Commenters
questioned the proposed rule’s assertion
that the Tongass should be managed
locally suggesting it ignores the Forest
Service’s 2001 conclusion that national
rulemaking was needed to protect
roadless areas.
As noted above, the unique
circumstances of the Tongass National
Forest have been recognized and
assessed since the 2001 rulemaking.
Then, as now, inclusion of the Tongass
National Forest under the national rule
was not mandatory but represented a
policy choice, as did the national rule
itself. In 2001 the Department
eventually opted for inclusion of the
Tongass National Forest. In 2008 and
2012, two other states requested and
were granted the opportunity to
discontinue operation under the
national rule. Today, the USDA
concludes that the interests furthered by
the national rule are not improperly
undone by exempting a single forest that
is now, and will remain for the
foreseeable future, substantially
undeveloped and roadless. The estimate
of 49 miles of additional road
construction (from 994 to 1,043) spread
across 9 million acres of land, over the
next 100 years, will not undo the
national rule’s underlying goal of
protecting roadless area characteristics
within the NFS, and moreover are well
within the USDA’s discretion to further
in light of the mix of mandates and
policy discretion embodied in the
relevant governing statutory provisions.
Comments on the administrative
change procedure. Commenters were
concerned with the administrative
change instruction for the lands suitable
for timber production in the Forest Plan,
alleging it is inconsistent with the
National Forest System Land
Management Planning regulations at 36
CFR part 219 (2012 Planning Rule) and
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would require an amendment. In
addition, commenters were concerned
that the agency did not include this
aspect of the rule during scoping.
The administrative change provision
at 36 CFR 219.13(c) clearly states that an
administrative change includes changes
to conform to new regulatory
requirements. Although the provision
was not expressly included in the
proposed action during scoping, it was
highlighted in the DEIS and conforms to
the requirements of the NEPA
implementing regulations.
Comments on subsistence mitigation.
Commenters allege that the Forest
Service violated ANILCA and NEPA by
refusing to consider updating the
roadless inventory to include lands
important to the Organized Village of
Kake, mitigation measures proposed by
Kake, and allowing a greater
management role for Kake in their
traditional territory.
The roadless inventories were
updated and additional areas were
included in Alternatives 2 and 3 as
designated Alaska Roadless Areas. All
unroaded areas were reviewed and some
areas identified in the 2003 and 2008
roadless analyses associated with
Tongass forest planning efforts were
included. In addition, small islands
previously excluded from roadless
designation were included if not
substantially altered.
Mitigation measures such as
identifying specific road segments,
selling carbon credits, and workforce
development are outside the scope of
the Alaska roadless rulemaking, which
is programmatic and does not evaluate
projects or partnerships.
Co-management of the Tongass
National Forest with tribal partners was
considered as an alternative but
eliminated from detailed analysis as it
does not comport with existing legal
authorities.
Comments on the site-specificity and
qualitative nature of the impact
analyses. The analyses in the FEIS are
a generalized review which the Council
on Environmental Quality recognizes as
appropriate for any broad or high-level
NEPA review of proposed policies,
plans, programs, or projects. It is
reasonable and efficient to limit detailed
site-specific impact analyses to when
specific proposals are brought before the
agency. Locations of potential timber
harvest and road construction are not
known at this time. While locations of
other developments, such as a regional
energy or transportation project, may be
more predictable based on published
information, it is not known if, when, or
specifically where they would occur.
When specific timber harvest or other
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projects are proposed, site-specific
NEPA analysis and required pubic
involvement would be conducted at that
time. No on-the-ground actions are
authorized by the final rule.
Comments on the adequacy of the
impact analyses. Commenters variously
questioned the adequacy of the impact
analyses, disagreed with the
conclusions made, and contended that
the effects are understated. Commenters
noted the obvious impacts of past
timber harvesting and road construction
as evidence the impacts were
understated. In addition, commenters
noted that the basis of the 2001 Roadless
Rule was the recognition that timber
harvesting and road construction were
impactful to roadless area values and
characteristics.
USDA does not dispute that timber
harvesting and road construction impact
roadless area values and characteristics.
However, the impact analyses in the
Rulemaking for Alaska Roadless Areas
DEIS and FEIS do not analyze the effects
of harvesting timber and constructing
roads in a specific roadless area. Rather,
the DEIS and FEIS analyze the
difference in effects under the 2001
Roadless Rule, the current Tongass
Forest Plan, and the other action
alternatives. The baseline for
comparison of alternatives is not a
pristine wilderness. Rather it is the
continuation or adjustment of current
management. Under the 2001 Roadless
Rule and Tongass Forest Plan, the Forest
Service projects the harvest of about 46
MMBF of timber per year across 227,000
available acres of old-growth and
334,000 available acres of young-growth
lands with about 994 miles of new road
construction across the 100-year
analysis period. Under the final rule
(Alternative 6) the agency projects the
harvest of about 46 MMBF of timber per
year across 395,000 available acres of
old-growth and 354,000 available acres
of young-growth lands with about 1,043
miles of new road construction across
the 100-year analysis period.
In addition, the impact analyses
considered the continuation of the
young-growth transition strategy in all
alternatives analyzed, including the noaction alternative and the final rule
alternative. The young-growth transition
strategy defines a 16-year period starting
in 2016 in which the old-growth
contribution to the projected timber sale
quantity decreases over time as younggrowth matures and becomes more
economical to harvest. At year 16, the
old-growth contribution to the projected
timber sale quantity would stabilize at
5 MMBF per year. The young-growth
transition strategy has a large beneficial
environmental effect on roadless areas
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because it shifts the focus of the Tongass
timber sale program to young-growth
areas which are largely already roaded.
In addition, the smaller contribution of
old-growth to the projected timber sale
quantity makes roadless areas less
economical because there are fewer
acres of old-growth to off-set the high
cost of road construction in the Tongass
National Forest. Old-growth is generally
more profitable than young-growth to
harvest due to higher volume per acre
and the higher value of the larger trees.
The impact analyses in the FEIS is
reflective of the small change between
the baseline and the action alternatives,
and the impact of the young-growth
transition strategy.
Comments on cost-benefit analysis.
Commenters expressed concern about
the cost-benefit analysis using changes
in suitable old-growth and younggrowth acres as an indicator for
potential displacement of recreationists
interested in primitive recreation
experiences. Primitive recreation is a
class of recreation utilized to describe
and manage recreation opportunities.
Primitive recreation opportunities occur
more than 3 miles from a road or
motorized trail; in areas generally
greater than 5,000 acres; where social
setting provide for less than 6 party
encounters on a trail; and are nonmotorized, typically include hiking,
horse packing, fishing, hunting, and
camping. There was concern about the
methodology used to measure adverse
visitor impacts. Commenters sought
consideration of scenic values in the
cost-benefit analysis. Commenters also
sought a cost-benefit economic analysis
that uses best available science to assess
socioeconomic impacts of each
alternative as well as analysis of the
socioeconomic value and impact on
fisheries, ecotourism, special use
permits, recreation, game populations,
and subsistence resources. Other
commenters expressed concern about
the inclusion of harvesting costs (felling,
yarding, and loading) and recreation
expenditures, as a distributional impact,
in the cost-benefit analysis.
In response to public comment, the
analysis of recreation visitation related
displacement and associated
expenditures, in the Regulatory Impact
Analysis (RIA), has been updated based
on new information received during
proposed and final rule preparation.
Scenic values, game species, and
subsistence are discussed qualitatively
in the RIA and examined in more detail
in the EIS. A cost-benefit analysis has
also been included in the RIA with new
data and information received during
proposed and final rule preparation.
This analysis includes benefits from a
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more efficiently managed timber sale
program alongside agency costs, forgone
conservation value, and costs of
potentially displaced recreationists. The
revised RIA includes discussion and
analysis of costs from felling, yarding,
and loading timber and acknowledges
their limited scope alongside other costs
to the timber industry and costs to the
agency from road maintenance. In
addition, detail has been added to the
RIA, noting that road cost changes
before and after 2011 were twice as high
during the exemption, and the relevance
of these costs alongside haul cost
savings. Potential recreation related
revenue losses can be considered
distributional if there are substitute
opportunities in southeast Alaska or on
the Tongass National Forest. However,
in some cases visitors may choose to not
come to southeast Alaska due to impacts
from harvesting and road construction;
thus, these estimates are appropriate for
inclusion in the costs and benefits
analysis.
Comments on ecosystem services.
Commenters sought an effects analysis
disclosing how the rule will directly
and indirectly impact ecosystem
services in the region, including
economic cost and benefits related to
impacts on ecosystem services. There
was concern that exemption from the
rule could lead to removal of trees and
damage to ecosystems which can
adversely impact ecosystem services.
In response to the comments received,
additional qualitative information and
discussion related to biological and
physical ecosystem services values has
been added to the RIA between
proposed and final rule preparation. In
addition, the cost-benefit analysis
includes quantitative estimates of
forgone conservation value, from peer
reviewed research designed to facilitate
the consideration of ecosystem services
in land management. Cost of forgone
conservation value are applied to the
net-change in suitable old-growth acres
across the alternatives. While only a
portion of suitable acres will be
harvested, the analysis includes an
upper estimate of value associated with
all suitable old-growth acres and a lower
estimate assuming all suitable oldgrowth acres would be harvested over
100 years. This range of estimates
accounts for uncertainty application of
value associated with conservation
demand.
Comments on road costs. Commenters
sought cost data for road building and
maintenance (per mile) in the areas
considered for exemption from the rule.
The RIA for the final rule includes
new information on road costs. Road
construction and decommissioning
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costs are not considered since it is
unlikely that they would be paid by the
agency given the influence of the
limited export policy. In 2007, the
Forest Service approved a limited
export policy, and this boost to
appraised values has made rare the
construction of roads by the agency in
advance of timber sales. Road
maintenance costs are considered
quantitatively in the cost-benefit
analysis of the final rule and regulatory
alternatives.
Comments on agency costs.
Commenters were concerned that the
reduction in expenses from exempting
the Tongass from the 2001 Roadless
Rule were not quantified. In addition,
commenters disagreed with the
assertion that the rule would not
increase agency costs because it would
not increase timber harvest levels and
sought a more comprehensive estimate
of anticipated agency costs and losses
from below-cost timber sales. In
addition, commenters asserted that
analysis should include an overall
assessment of the Tongass timber
program costs including road costs. In
addition, commenters noted the agency
costs section should also include the
estimated cost for conducting this
rulemaking.
Details on agency costs from road
maintenance have been added to the
RIA for the final rule in the RIA section
called ‘‘Agency Costs including Control
of Regulatory Costs’’. Detailed analysis
of reductions in environmental
compliance cost are not possible. This
final rule and the regulatory alternatives
are programmatic, meaning that they
establish direction for broad land areas,
rather than schedule specific activities
in specific locations. None of the
alternatives authorize any site-specific
projects or other ground-disturbing
activities and, therefore, it is not
possible to estimate future activities and
subsequent marginal changes in
environmental activities. However,
potential incremental reductions in
compliance costs are noted in the RIA
for the final rule. The cost of rulemaking
is the cost of managing NFS lands as a
part of normal agency operation and
exists as part of the baseline 2001
roadless rule so there are not
incremental costs.
Comments on recreation and tourism.
Some commenters suggested that the
recreation-related assessment provided
in the RIA understated potential
impacts to the visitor industry because
it considers only changes in suitable
timber acres and does not address
indirect effects to adjacent areas,
whereas, timber harvest and road
construction have the potential to affect
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much larger areas than the area that is
logged. In addition, commenters
expressed concern that the Forest
Service did not analyze the
corresponding effects on rural
communities from the displacement of
outfitters, guides, and tour operators.
The analysis of recreation in the RIA
for the final rule is not a site-specific
review; rather, it uses available
information to illustrate broad patterns
of use and differentiate between the
regulatory alternatives. It assumes all
visitation, and half of visitation, is
displaced under the highest level of
timber suitability designation, under the
final rule, to provide an upper- and
lower estimate of displacement, for a
broad orders of magnitude comparison
with other costs and benefits. Assuming
all visitation is displaced considers not
just effects on visitation occurring
physically on lands suitable for timber
production but also effects on visitation
in other areas. The revised analysis also
includes assessing the economic
importance of nature-based tourism in
southeast Alaska, as measured by
business revenue, from data collected by
the University of Alaska, Anchorage.
Comments on the DEIS climate and
carbon analysis. Commenters were
concerned that the DEIS analysis did
not utilize the best available science and
the qualitative nature of the analysis is
not sufficient.
The climate and carbon analysis in
the DEIS and FEIS is based on the best
available science on carbon stocks and
fluxes, and is consistent with the latest
literature including the Pacific
Northwest Research Station’s Science
Findings that became available after
publication of the DEIS (Forestry as a
Natural Climate Solution: The Positive
Outcomes of Negative Carbon
Emissions, March 2020). The DEIS and
FEIS analysis utilized Forest Inventory
and Analysis data sets specific to the
Tongass National Forest to assess forest
carbon stocks and disturbance trends
over a recent 20-year period. The
influence of potential future climate on
the Forest was detailed using recent
global circulation model projections and
relevant scientific literature detailing
climate impacts.
The foreseeable impacts of the final
rule on carbon emissions and forest
carbon stocks are extremely small
because the level of timber harvesting is
expected to be the same between
implementation of the 2001 Roadless
Rule and a full exemption. Therefore, a
qualitative approach is appropriate and
sufficient.
Comments on the DEIS timber
analysis—level of harvest. Commenters
were concerned that the timber analysis
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assumed no increased level of timber
harvest.
The level of harvest used in the DEIS
and FEIS timber analysis is based on the
Forest Plan projected timber sale
quantity of 46 MMBF feet per year. This
is a reasonable, conservative assumption
for the analysis because it is based on
estimates of long-term market demands.
The Tongass National Forest actual
volume sold was approximately 30.9
MMBF in fiscal year 2017, 9.3 MMBF in
fiscal year 2018, and 5.6 MMBF in fiscal
year 2019. Thus, 46 MMBF remains a
reasonable estimate to utilize for effects
analyses based on volume sold since
2016, when the forest plan was most
recently amended, and more
importantly it remains the agency’s best
estimate despite a few years of lower
harvest levels.
The USDA recognizes the projected
timber sale quantity is not a cap, like the
allowable sale quantity from the 1982
Planning Rule. It is only an estimate,
and at this time it is the agency’s best
estimate.
The agency has no reason to believe
harvest levels will increase from the
2016 Forest Plan annual projected
timber sale quantity based on
implementation of the final rule.
Although, the final rule will increase
the acres of old-growth available for
harvest by about 168,000 acres, this
opportunity is likely to be constrained
by the implementation of the younggrowth transition strategy and the
economics of timber harvesting in
general. As previously mentioned, after
2032 the transition old-growth timber
harvest will be limited to 5 MMBF per
year, at which point entry into roadless
areas will become less attractive because
there will be fewer high-volume acres to
off-set the cost of new road
construction. As the young-growth
matures and becomes a greater
proportion of the annual harvest, the
Tongass timber sale program will
become more focused on previously
roaded areas, where the majority of the
young-growth stands exist. In addition,
between 2003 and 2011 when the
Tongass National Forest was exempted
from the 2001 Roadless Rule, only about
300 acres of timber were harvested
within IRAs. This indicates that there
will likely not be a rush to harvest old
growth within roadless areas under the
final rule.
Comments on the DEIS timber
analysis—distribution of harvest.
Commenters were concerned that the
DEIS timber analysis assumed oldgrowth and young-growth harvest
would be evenly disturbed across
suitable acres. Commenters were
concerned this made it difficult to fully
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understand the impacts of the
alternatives to a community.
Based on these concerns, the timber
analysis was refined to estimate where
old growth is most likely to be harvested
within the suitable acreage over the next
100 years. Estimates considered timber
sale economics, old-growth volume, and
timber sale history on the Tongass
National Forest. The result of the
analysis is a shift of expected timber
harvest from the northern ranger
districts to the southern ranger districts.
The biggest declines in the north are in
the Sitka and Hoonah ranger districts,
and the largest increases are in the
Thorne Bay and Petersburg ranger
districts.
Comments regarding environmental
justice. Commenters expressed concerns
that tribal members rely on roadless
areas for food security, cultural
practices, and their traditional way of
life and that the final rule would
disproportionately impact them, which
would be a violation of environmental
justice principles.
The final rule is programmatic and, as
such, does not schedule specific
activities in specific locations. The final
rule will increase the acres available for
timber harvest, but harvest levels are
expected to remain the same as they
would under the 2001 Roadless Rule.
The amount of new or reconstructed
road miles is expected to be similar as
the 2001 Roadless Rule. This makes it
challenging to evaluate the effects of the
final rule on communities or
populations. However, the Civil Rights
Impact Analysis (Departmental
Regulation 4300–004) recognizes that
although the rule itself does not have a
disproportionate effect on any specific
population, specific activities associated
with implementation of the Forest Plan
within roadless areas can have
environmental justice implications. An
opportunity for review for
environmental justice concerns will be
available if and when activities are
proposed, and specific locations and
extent are defined.
Regulatory Certifications
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Regulatory Planning and Review
The OMB determined this rulemaking
to be a significant regulatory action as
it may raise novel legal or policy issues
arising out of legal mandates, the
President’s priorities, or the principles
set forth in Executive Order 12866. The
agency has prepared a regulatory
requirements analysis of impacts and
discussion of benefits and costs of the
final rule.
The final rule exempting the Tongass
National Forest from the 2001 Roadless
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Rule will provide additional
opportunities for timber harvest and
road construction to occur; however, it
does not materially affect the total
quantity of timber expected to be
harvested or miles of new roads
constructed. As to timber harvest
activities, the final rule would increase
the flexibility for land managers to
locate and design timber sales.
Improved flexibility could, in turn,
improve the Forest Service’s ability to
offer economic sales that meet timber
industry needs and contribute to rural
economies. While many factors can
influence the cost of timber harvest,
areas along existing roads or those using
marine access facilities are typically
more economically efficient, followed
by areas where existing roads can be
easily extended. The most expensive
harvesting costs are associated with
areas without existing road or marine
access facilities.
Cost savings from improved flexibility
for timber harvest activities would
accrue alongside other benefits,
including reduced costs for leasable
mineral availability and increased
potential for development of renewable
energy and transportation projects.
While many of these activities were
allowed under the 2001 Roadless Rule,
industry advocates believe that the 2001
Roadless Rule discouraged private
sector investment in projects within
roadless areas. Although it is difficult to
estimate the extent of investments that
did not occur due to fear of regulatory
burden, the perception of this does
affect the level of investment, and the
final rule will eliminate that concern.
Stumpage value benefits are
quantified alongside agency road
maintenance costs, cost of forgone
conservation value, estimated lost
revenue to outfitters and guides from
visitors potentially displaced by annual
harvest of suitable young- and oldgrowth, and forgone value of access to
recreationists not using outfitter and
guides. Dollars spent by visitors are not
necessarily lost but subject to
displacement-related changes. Some
businesses may lose revenue if visitors
choose not to travel to southeast Alaska,
but others may see increases in revenue
if visitors choose to stay longer or travel
to substitute sites within southeast
Alaska. Discounted upper bound
estimates of net present value are
positive for the final rule and regulatory
alternatives.
Regulatory Flexibility Act and
Consideration of Small Entities
The USDA certifies that the final rule
does not have a significant economic
impact on a substantial number of small
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68701
entities as determined in the Regulatory
Flexibility Analysis because the final
rule does not directly subject small
entities to regulatory requirements.
Therefore, notification to the Small
Business Administration’s Chief
Council for Advocacy is not required
pursuant to Executive Order 13272. A
number of small and large entities may
experience time or money savings as a
result of flexibility provided by the final
rule, or otherwise benefit from activities
on NFS lands under the final rule.
Paperwork Reduction Act
This final rule does not require any
additional record keeping, reporting
requirements, or other information
collection requirements as defined in 5
CFR part 1320 that are not already
approved for use and, therefore,
imposes no additional paperwork on the
public. Accordingly, the review
provisions of the Paperwork Reduction
Act of 1995 (44 U.S.C. 3501 et seq.) and
its implementing regulations at 5 CFR
part 1320 do not apply.
Regulatory Risk Assessment
A risk assessment is only required
under 7 U.S.C. 2204e for a ‘‘major’’ rule,
the primary purpose of which is to
regulate issues of human health, human
safety, or the environment. The statute
(Pub. L. 103–354, Title III, Section 304)
defines ‘‘major’’ as any regulation the
Secretary of Agriculture estimates is
likely to have an impact on the U.S.
economy of $100 million or more as
measured in 1994 dollars. Economic
effects of the final rule are estimated to
be less than $100 million per year.
Reducing Regulation and Controlling
Regulatory Costs
Executive Order 13771, Reducing
Regulation and Controlling Regulatory
Costs, issued January 30, 2017, requires
that significant new regulations shall, to
the extent permitted by law, be offset by
the elimination of existing costs
associated with at least two prior
regulations.
The final rule has been reviewed in
accordance with Executive Order 13771
on reducing regulation and controlling
regulatory costs and is considered an
Executive Order 13771 deregulatory
action.
Federalism
The USDA has considered the final
rule in context of Executive Order
13132, Federalism, issued August 4,
1999. The USDA has determined the
final rule conforms with federalism
principles set out in Executive Order
13132, would not impose any
compliance costs on any state, and
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would not have substantial direct effects
on states, on the relationship between
the National Government and the State
of Alaska, or any other state, nor on the
distribution of power and
responsibilities among the various
levels of government. Therefore, the
USDA concludes that this final rule
does not have federalism implications.
The final rule is based on a petition
submitted by the State of Alaska under
the APA (5 U.S.C. 553(e)) and pursuant
to USDA regulations at 7 CFR 1.28. The
final rule responds to the State of
Alaska’s petition, considers public
comment received during the Forest
Service’s public comment periods, and
considers input received from
cooperating agencies. The State of
Alaska is a cooperating agency pursuant
to 40 CFR 1501.6 of the Council on
Environmental Quality regulations for
implementing the procedural provisions
of the NEPA.
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No Takings Implications
The USDA has considered the final
rule in context with the principles and
criteria contained in Executive Order
12630, Governmental Actions and
Interference with Constitutionally
Protected Property Rights, issued March
15, 1988. The USDA has determined
that the final rule does not pose the risk
of a taking of private property because
it only applies to management of NFS
lands and contains exemptions that
prevent the taking of constitutionally
protected private property.
Consultation With Indian Tribal
Governments
On July 30, 2018, the Forest Service
initiated government-to-government
consultation with 32 Alaska federally
recognized tribes and 27 Alaska Native
corporations, and invited them to
participate as cooperating agencies
during the rulemaking process. Six
tribes initially agreed to become a
cooperating agency including Angoon
Community Association, Central
Council Tlingit and Haida Indian Tribes
of Alaska, Hoonah Indian Association,
Hydaburg Cooperative Association,
Organized Village of Kake, and
Organized Village of Kasaan. The
Organized Village of Kake withdrew as
a cooperating agency after publication of
the proposed rule, and the remaining
tribal cooperating agencies withdrew
after the publication of the FEIS in
collective protest over the identification
of the full exemption alternative as the
preferred alternative in the FEIS.
Periodic cooperating agency meetings
were held throughout the rulemaking
process that included the tribal
cooperating agencies. Furthermore,
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government-to-government
consultations occurred by request and
twelve consultation meetings were held
throughout the rulemaking process. Two
of the twelve government-to-government
consultation meetings were conducted
by USDA Under Secretary James
Hubbard and the remaining ten
meetings were conducted by the Alaska
Region of the Forest Service.
On July 21, 2020, the Secretary of
Agriculture received a petition from
nine southeast Alaska Tribal
governments, requesting the United
States government to commence a new
rulemaking in collaboration with Tribes
to create a Traditional Homelands
Conservation Rule to identify and
protect traditional and customary uses
of the Tlingit, Haida, and Tsimshian
peoples in the Tongass National Forest.
This petition also requests the USDA
create a new process for engaging in
consultation with Tribes based on the
principle of ‘‘mutual concurrence’’. The
petition states that it was submitted in
response to the Tribes’ experience in the
Alaska Roadless Rulemaking process
and their belief that their contributions
were not adequately considered. The
petition is currently under review by the
Secretary.
The final rule was reviewed in
accordance with the requirements of
Executive Order 13175, Consultation
and Coordination with Indian Tribal
Governments. Executive Order 13175
requires federal agencies to consult and
coordinate with tribes on a governmentto-government basis on policies that
have tribal implications, including
regulations, legislative comments, or
proposed legislation, and other policy
statements or actions that may have
substantial direct effects on one or more
Indian tribes, on the relationship
between the Federal Government and
Indian tribes, or on the distribution of
power and responsibilities between the
Federal Government and Indian tribes.
The USDA’s Office of Tribal Relations
assessed the impact of the final rule on
Indian tribes and determined the final
rule has tribal implications that require
continued outreach efforts in the
implementation of the final rule to
determine if tribal consultation under
Executive Order 13175 is required. To
date, as part of the regulatory review
process noted above, the Forest Service
conducted various outreach efforts to
American Indian and Alaska Native
tribes, villages, and corporations
regarding the development of this final
rule, and the tribal cooperation in this
process.
If a tribe requests consultation, the
Forest Service will work with the USDA
Office of Tribal Relations to ensure
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meaningful consultation is provided
where changes, additions, and
modifications identified herein are not
expressly mandated by Congress.
Civil Justice Reform
The USDA reviewed the final rule in
context of Executive Order 12988. The
USDA has not identified any state or
local laws or regulations that conflict
with the final rule or would impede full
implementation of the rules. However, if
the rule is adopted, all state and local
laws and regulations that conflict with
this rule or would impede full
implementation of this rule would be
preempted. No retroactive effect would
be given to this rule, and the final rule
would not require the use of
administrative proceedings before
parties could file suit in court.
Unfunded Mandates
Pursuant to Title II of the Unfunded
Mandates Reform Act of 1995 (2 U.S.C.
1531–1538), signed into law on March
22, 1995, the USDA has assessed the
effects of the final rule on state, local,
and tribal governments and the private
sector. The final rule does not compel
the expenditure of $100 million or more
by any state, local, or tribal government,
or anyone in the private sector.
Therefore, a statement under section
202 of the Act is not required.
Energy Effects
The USDA has considered the final
rule in context of Executive Order
13211, Actions Concerning Regulations
That Significantly Affect Energy Supply,
Distribution, or Use, issued May 18,
2001. The USDA has determined the
final rule does not constitute a
significant energy action as defined in
Executive Order 13211. Therefore, a
statement of energy effects is not
required.
E-Government Act
The USDA is committed to complying
with the E-Government Act, to promote
the use of the internet and other
information technologies to provide
increased opportunities for citizen
access to government information and
services, and for other purposes.
List of Subjects in 36 CFR Part 294
National forests, Navigation (air),
Recreation areas, Roadless area
management.
For the reasons set forth in the
preamble, the USDA amends part 294 of
title 36 of the Code of Federal
Regulations by adding subpart E,
consisting of §§ 294.50 and 294.51, to
read as follows:
■
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§ 294.51
PART 294—SPECIAL AREAS
Subpart E—Alaska Roadless Areas
Management
Authority: 16 U.S.C. 472, 529, 551, 1608,
1613; 23 U.S.C. 201, 205.
§ 294.50
Tongass National Forest.
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Subpart B of this part, revised as of
July 1, 2001, shall not apply to the
Tongass National Forest.
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Transition.
The Tongass Forest Supervisor shall
issue a ministerial Notice of
Administrative Change pursuant to 36
CFR 219.13(c) identifying plan changes
made in conformance with the
regulatory determinations of this
subpart; specifically, the portion of the
December 9, 2016, Record of Decision
concerning suitable timber lands
attributed exclusively to
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68703
implementation of the January 12, 2001,
Roadless Area Conservation Rule (see 36
CFR part 294, revised as of July 1, 2001)
shall be designated as suitable.
Dated: October 26, 2020.
Stephen Censky,
Deputy Secretary of Agriculture.
[FR Doc. 2020–23984 Filed 10–28–20; 8:45 am]
BILLING CODE 3411–15–P
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Agencies
[Federal Register Volume 85, Number 210 (Thursday, October 29, 2020)]
[Rules and Regulations]
[Pages 68688-68703]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2020-23984]
[[Page 68687]]
Vol. 85
Thursday,
No. 210
October 29, 2020
Part III
Department of Agriculture
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Forest Service
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36 CFR Part 294
Special Areas; Roadless Area Conservation; National Forest System Lands
in Alaska; Final Rule
Federal Register / Vol. 85 , No. 210 / Thursday, October 29, 2020 /
Rules and Regulations
[[Page 68688]]
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DEPARTMENT OF AGRICULTURE
Forest Service
36 CFR Part 294
RIN 0596-AD37
Special Areas; Roadless Area Conservation; National Forest System
Lands in Alaska
AGENCY: Forest Service, Agriculture Department (USDA).
ACTION: Final rule and record of decision.
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SUMMARY: The U.S. Department of Agriculture (USDA or Department), is
adopting a final rule to exempt the Tongass National Forest from the
2001 Roadless Area Conservation Rule (2001 Roadless Rule), which
prohibits timber harvest and road construction/reconstruction with
limited exceptions within designated inventoried roadless areas. In
addition, the rule directs an administrative change to the timber
suitability of lands deemed unsuitable, solely due to the application
of the 2001 Roadless Rule, in the 2016 Tongass National Forest Land and
Resource Management Plan (Tongass Forest Plan or Forest Plan), Appendix
A. The rule does not authorize any ground-disturbing activities, nor
does it increase the overall amount of timber harvested from the
Tongass National Forest.
DATES: This rule is effective October 29, 2020.
FOR FURTHER INFORMATION CONTACT: Ken Tu, Interdisciplinary Team Leader,
at 303-275-5156 or [email protected]. Individuals using
telecommunication devices for the deaf (TDD) may call the Federal
Information Relay Services at 1-800-877-8339 between 8 a.m. and 8 p.m.
Eastern Time, Monday through Friday.
SUPPLEMENTARY INFORMATION: The USDA Forest Service manages
approximately 21.9 million acres of federal lands in Alaska, which are
distributed across two national forests (Tongass and Chugach National
Forests). These national forests are characterized by a diverse array
of landscapes, ecosystems, natural resources, and land use activities.
In January 2001, the USDA promulgated a discretionary rulemaking
establishing prohibitions on timber harvesting and road construction on
approximately 58 million acres of the National Forest System (NFS),
including over 14 million acres within Alaska. The 2001 Roadless Rule
has been the subject of litigation for almost two decades. Initially,
the 2001 Roadless Rule was challenged in multiple lawsuits, including a
suit brought by the State of Alaska. Another suit filed by the State of
Alaska in 2015 is still ongoing. Citing various concerns, including
damage to the economic and social fabric of southeast Alaska and
compliance with the Alaska National Interest Lands Conservation Act
(ANILCA) and Tongass Timber Reform Act (TTRA), the State of Alaska
petitioned the USDA to exempt the Tongass National Forest from the 2001
Roadless Rule.
Having carefully considered the petition, public comments on the
proposed rule, and a wide range of alternative approaches to the 2001
Roadless Rule, the USDA is granting the State of Alaska's request to
exempt the Tongass National Forest from the 2001 Roadless Rule. The
Tongass Forest Plan along with other conservation measures, will assure
protection allowing roadless area values to prevail on the Tongass
National Forest while offering additional flexibility to achieve other
multiple-use benefits.
Background
On January 12, 2001, the USDA promulgated the Roadless Area
Conservation Rule (hereafter 2001 Roadless Rule) (66 FR 3244),
establishing nationwide prohibitions on timber harvest, road
construction, and road reconstruction within inventoried roadless areas
(IRAs) with certain limited exceptions. The intent of the 2001 Roadless
Rule is to provide lasting protection for IRAs within the NFS in the
context of multiple-use land management. Based on the State of Alaska's
Roadless Rule Petition (described below) and a review of public
comment, the USDA analyzed rulemaking alternatives addressing whether
and how the national prohibitions on timber harvesting, road
construction, and road reconstruction should apply on the Tongass
National Forest.
In 2001, the State of Alaska filed a lawsuit challenging the USDA's
promulgation of the 2001 Roadless Rule and its application in Alaska.
State of Alaska v. USDA, A01-039 CV (JKS) (D. Alaska). The USDA and the
State of Alaska reached a settlement in 2003, and the USDA subsequently
issued a rule temporarily exempting the Tongass National Forest from
the 2001 Roadless Rule. In 2011, a Federal district court set aside the
Tongass Exemption Rule and reinstated, with clarifying instructions,
the 2001 Roadless Rule on the Tongass National Forest. The district
court's ruling was initially reversed by a three-judge panel of the
Ninth Circuit but was ultimately upheld in a 6-5 en banc ruling in
2015. Consequently, the 2001 Roadless Rule (as provided for in the
district court's Judgment) remains in effect in Alaska and the Forest
Service continues to apply the 2001 Roadless Rule to both the Tongass
and Chugach National Forests.
Currently there are over 21.9 million acres of NFS lands within the
State of Alaska, of which approximately 14.7 million acres (67%) are
designated IRAs as defined by the 2001 Roadless Rule, including both
the Tongass and Chugach National Forests. The Tongass National Forest
is approximately 16.7 million acres of which approximately 9.3 million
(55%) acres are designated IRAs. The Alaska Roadless Rule focuses on
the Tongass National Forest only and does not apply to the Chugach
National Forest.
State of Alaska Petition
In January 2018, then-Commissioner of the Department of Natural
Resources for the State of Alaska, Andrew Mack submitted a petition on
behalf of the State of Alaska to Secretary of Agriculture Sonny Perdue
pursuant to the Administrative Procedure Act (APA). The petition
requested USDA consider creation of a state-specific rule to exempt the
Tongass National Forest from the 2001 Roadless Rule and conduct a
forest plan revision for the Tongass National Forest. In June 2018, the
Secretary of Agriculture accepted the petition and agreed to review the
State's concerns on roadless area management and economic development
opportunities in southeast Alaska through a rulemaking process. The
Secretary directed the Forest Service to begin working with
representatives from the State of Alaska concerning a state-specific
roadless rule. However, the Secretary did not commit to the State's
request for a forest plan revision. On August 2, 2018, the State of
Alaska and the USDA Forest Service signed a memorandum of understanding
concerning the development of a state-specific rule. The Forest Service
initiated its environmental analysis process with the publication in
the Federal Register of a Notice of Intent (NOI) to prepare an
environmental impact statement (EIS) on August 30, 2018 (83 FR 44252).
On September 6, 2018, Governor Walker issued Administrative Order
299 to establish the Alaska Roadless Rule Citizen Advisory Committee
(the committee) to provide an opportunity for Alaskans to advise the
State of Alaska on the future management of Tongass National Forest
roadless areas. The committee was comprised of 13 members, appointed by
Governor
[[Page 68689]]
Walker, intended to represent a diversity of perspectives, including
Alaska Native tribes and corporations, fishing, timber, conservation,
tourism, utilities, mining, transportation, local government, and the
Alaska Division of Forestry. The committee's specific task was to
present a written report on the rulemaking process to the Governor and
State Forester, which included options for a state-specific roadless
rule. The committee met for three in-person meetings during the fall of
2018 (October 2-3 in Juneau; October 24-26 in Ketchikan; and November
6-8 in Sitka). Meetings were open to the public and each meeting
included opportunity for public comment. The committee's report was
submitted to the Governor and State Forester during late November 2018,
and recommendations from the committee informed the State of Alaska
input, as a cooperating agency, to the Forest Service in the
development of the alternatives and comments on the Draft Environmental
Impact Statement (DEIS).
On October 17, 2019, the USDA published a notice of proposed
rulemaking to exempt the Tongass National Forest from the 2001 Roadless
Rule (84 FR 55522). The Office of Federal Activities of the U.S.
Environmental Protection Agency published a Notice of Availability
(NOA) for the DEIS in the Federal Register on October 18, 2019 (84 FR
55952), with corrected end of comment period published on October 25,
2019 (84 FR 57417).
Consideration of the State of Alaska's Petition
In response to the State of Alaska's petition for rulemaking, the
USDA has sought a long-term, durable approach to roadless area
management that accommodates the unique biological, social, and
economic situation found in and around the Tongass National Forest. The
Tongass is unique from other national forests with respect to size,
percentage of IRAs, number of communities dependent on federal lands
(the Tongass comprises almost 80% of southeast Alaska and supports 32
communities), and Alaska and Tongass-specific statutory considerations
(e.g., ANILCA, TTRA).
The USDA and Forest Service believe that both roadless area
conservation and other multiple-use values with important local socio-
economic consequences are meaningfully addressed through local and
regional forest planning on the Tongass, without the 2001 Roadless Rule
prohibitions on timber harvest and road construction/reconstruction.
Decision
The USDA hereby promulgates a regulation exempting the Tongass
National Forest from the 2001 Roadless Rule as described in Alternative
6 of the Rulemaking for Alaska Roadless Areas Final Environmental
Impact Statement (FEIS) (USDA Forest Service, 2020). This decision is
not subject to Forest Service administrative review regulations, which
allow the public to administratively challenge certain agency
decisions. In addition, the final rule directs the Tongass Forest
Supervisor to issue a notice of an administrative change pursuant to 36
CFR 219.13(c) to the timber suitability determination as described in
Appendix A of the Forest Plan. The final regulatory text differs
slightly from the text published with the FEIS, reflecting nontechnical
changes made to conform to the Office of Federal Register's guidelines.
Alternatives Considered
In addition to Alternative 6, the selected alternative, the FEIS
analyzes five other alternatives for managing roadless areas on the
Tongass National Forest. Alternative 1 is the no action alternative and
would result in the continued implementation of the 2001 Roadless Rule
as prescribed in the Alaska District Court's Judgement. Alternative 2
provides limited additional timber harvest opportunity while maximizing
roadless area designations. It removes approximately 142,000 acres from
roadless designation that have been substantially altered by prior road
construction or timber harvest generally conducted during periods of
time the Tongass National Forest was exempted from the 2001 Roadless
Rule. These substantially altered areas are generally known as ``roaded
roadless'' acres, but include additional areas considered to be
substantially altered. Alternative 2 also adds 110,000 acres as Alaska
Roadless Areas. Following an approach similar to that taken for the
other two State-specific roadless rules, Colorado and Idaho, the FEIS
uses the term Alaska Roadless Areas to refer to the areas in which the
Alaska Roadless Rule would apply in Alternatives 2 through 5.
Alternative 3 would increase the available land base from which
timber harvest opportunities could occur by making timber harvest, road
construction, and road reconstruction permissible in areas where
roadless characteristics have already been substantially altered and
areas immediately adjacent to existing roads and past harvest areas.
Adjacent areas are considered to be the logical extensions of the
existing road and/or harvest systems, which would remove approximately
401,000 acres from the roadless classification system. The adjacent
areas represent the most likely locations where future timber harvest
could occur and have the least environmental impacts to overall
roadless characteristics while providing for additional timber harvest
opportunities.
Alternative 3 also establishes a Community Priority category which
allows for small-scale timber harvest and associated road construction
and reconstruction. In addition, it allows for infrastructure
development to connect and support local communities, recreation
opportunities, and traditional Alaska Native cultural uses. Alternative
3 includes the Watershed Priority category, which is more restrictive
than the 2001 Roadless Rule, and applied to approximately 3.26 million
acres primarily identified in the Forest Plan as the Tongass 77
Watersheds and The Nature Conservancy/Audubon Conservation Priority
Areas (T77 and The Nature Conservancy/Audubon Conservation Areas) and
high-priority sockeye salmon watersheds. Approximately 90% of those
3.26 million acres fall within roadless area boundaries identified in
Alternative 3. To provide heightened balance and integrity of watershed
protections and establish management continuity across these high-
priority watersheds, Alternative 3 would also include a prohibition on
old-growth timber harvesting on the portion of the T77 and The Nature
Conservancy/Audubon Conservation Areas that extend beyond roadless
areas boundaries established by Alternative 3. The remaining 4,595,000
acres of Alaska Roadless Areas in Alternative 3 would be managed under
a roadless management category called Roadless Priority, which is
similar to the 2001 Roadless Rule but less restrictive and addresses
Alaska-specific concerns for infrastructure development to connect and
support local communities and access to renewable energy and leasable
minerals.
In addition to roaded roadless and adjacent acres being removed
from the roadless classification system, approximately 854,000 acres
designated as land use designation (LUD) II areas would be removed from
the roadless classification system in Alternative 3. LUD II areas are
statutory land use designations managed in a roadless state to retain
their wildland character as defined in the TTRA (Pub. L. 101-626, Title
II, Section 201) and the National Defense Authorization Act for Fiscal
[[Page 68690]]
Year 2015 (Pub. L. 113-291, 128 Stat. 3729, Section 3720(f)). These
areas are proposed for removal from regulatory roadless classification
because having two layers of protection (statutory and regulatory
direction) that are substantially similar but slightly different does
not make a meaningful difference to the level of conservation provided
and can create confusion for land managers, stakeholder groups, and the
public. Removal of the LUD II areas from regulatory roadless
classification is an attempt to eliminate that confusion while
remaining consistent with the congressionally established management
regime for the LUD II areas. The statutory direction managing in a
roadless state for wildland character within LUD II areas would remain
in effect regardless of which alternative is selected.
Alternative 4 provides additional available land base from which
timber harvest opportunities could occur while maintaining roadless
designations for areas defined in the Tongass Forest Plan as Scenic
Viewsheds, T77 Watersheds, and The Nature Conservancy/Audubon
Conservation Priority Areas. Additional timber harvest opportunities
are provided by removing approximately 401,000 acres of roaded roadless
areas and adjacent extensions, as described in Alternative 3, from
roadless classification. In addition, timber harvest opportunities are
provided by managing approximately 757,000 acres of Timber Production
and Modified Landscape LUDs, as defined in the Tongass Forest Plan, in
a roadless management category called Timber Priority, which allows for
timber harvest, road construction, and road reconstruction.
Alternative 4 designates approximately 7,000 acres as Alaska
Roadless Areas, which were statutorily designated as LUD II areas, but
not included in the 2001 roadless inventory. These 7,000 acres combined
with the LUD II areas included in the 2001 roadless inventory total
854,000 acres that would be designated as roadless with regulatory
direction mirroring the statutory direction.
The remaining 7,363,000 acres of Alaska Roadless Areas in
Alternative 4 would be managed as Roadless Priority, which is similar
to the 2001 Roadless Rule, but less restrictive and addresses Alaska-
specific concerns for infrastructure development to connect and support
local communities and access to renewable energy and leasable minerals.
Alternative 5 maximizes the land base from which timber harvest
opportunities could occur by removing 2.32 million acres from roadless
area designation. Taken together, the six alternatives represent the
spectrum of management regimes identified to the Forest Service through
public comments, public meetings, tribal and Alaska Native corporation
consultations, and cooperating agency input.
The table below displays the acreage changes from the 2001 Roadless
Rule to acreages that would be designated under each of the six
alternatives displayed in the FEIS.
--------------------------------------------------------------------------------------------------------------------------------------------------------
Alternatives
-----------------------------------------------------------------------------------------------
1 2 3 * 4 5 6 Final rule
--------------------------------------------------------------------------------------------------------------------------------------------------------
Total Roadless Acres.................................... 9,368,000 9,336,000 8,224,000 8,975,000 7,047,000 0
Roadless Acres Removed.................................. 0 142,000 1,252,000 401,000 2,321,000 9,368,000
Roadless Acres Added.................................... 0 110,000 107,000 7,000 0 0
Net Acre Change **...................................... 0 -32,000 -1,144,000 -394,000 -2,321,000 -9,368,000
--------------------------------------------------------------------------------------------------------------------------------------------------------
* Alternative 3 has less total areas designated as roadless than Alternative 4 due to 854,000 of LUD II areas removed but they are still managed for
wildland character based on statutory direction, hence Alternative 3 is more restrictive than Alternative 4.
** Numbers may not appear to sum correctly due to rounding.
Environmentally Preferable Alternative
The environmentally preferable alternative is the alternative that
best promotes the national environmental policy as provided by Section
101 of the National Environmental Policy Act (NEPA), 42 U.S.C. 4331. In
application, the environmentally preferable alternative causes the
least damage to the biological and physical environment. It also best
protects, preserves, and enhances historic, cultural, and natural
resources. It is the alternative that achieves the widest range of
beneficial uses of the environment without degradation, risk to health
and safety, or other undesirable or unintended consequences.
Alternative 2 is the environmentally preferable alternative. While
it represents a slight decrease (approximately 32,000 acres) in total
acres to be managed as Alaska roadless areas, all the acres designated
as Alaska Roadless Areas in Alternative 2 are undeveloped at this time.
Alternative 1 (the 2001 Roadless Rule) includes more total roadless
acres; however, approximately 142,000 acres have been roaded,
harvested, or significantly altered and those lands no longer retain
the roadless characteristics and values the 2001 Roadless Rule is
intended to conserve. In addition, approximately 110,000 acres of
undeveloped land not included in the 2001 Roadless Rule were designated
as Alaska Roadless Areas. Alternative 2 limits timber harvesting, road
construction, and road reconstruction on the most undeveloped roadless
acres of all the alternatives considered. While the Roadless Priority
management category assigned to approximately 5.2 million acres in
Alternative 2 includes more exceptions than Alternative 1, the
Watershed Priority management category, which is more restrictive than
the 2001 Roadless Rule, is applied to approximately 3.3 million acres
in Alternative 2. For all these reasons, Alternative 2 is the
alternative that best protects, preserves, and enhances roadless
characteristics and values on the Tongass National Forest.
Decision Rationale and Important Considerations
On July 12, 2001, the 2001 Roadless Rule was promulgated. Views on
applying roadless restrictions on the Tongass National Forest changed
dramatically over the course of that rulemaking, and since. Originally,
the USDA's proposed rule sought to exclude the Tongass from any
roadless restrictions while promising to revisit the question in five
years. Seven months later, the USDA's Final EIS (FEIS) instead
identified a preferred alternative to apply the roadless prohibitions
after a five-year delay. A mere month later, the final Record of
Decision (ROD) instead elected to apply the regulation's roadless
prohibitions immediately upon the effective date of the rule.
In 2003, USDA settled litigation with the State of Alaska
challenging the promulgation of the 2001 Roadless Rule. The USDA
proposed and finalized a rule temporarily exempting the Tongass
[[Page 68691]]
National Forest from operation of the 2001 Roadless Rule (e.g., Tongass
Exemption Rule--68 FR 75136). However, the Tongass Exemption Rule
itself was judicially set aside in 2011, and the 2001 Roadless Rule was
reinstated under the terms set forth in the final judgment of the U.S.
District Court for the District of Alaska. Since that time, no further
regulatory action regarding this matter has taken place, and the 2001
Roadless Rule remains in effect as to the Tongass National Forest.
Considerable congressional interest has resulted in the
introduction of competing legislative bills designed to alternatively
codify or strike down the operation of the 2001 Roadless Rule, in whole
or in part, since the rule was promulgated. These legislative proposals
have included attempts to legislate an outcome for the rule's
application to the Tongass National Forest, but none of these bills
have been enacted into law.
Combined with the complex, and sometimes even conflicting, judicial
rulings applicable to the 2001 Roadless Rule itself, the recent history
of roadless management on the Tongass National Forest demonstrates that
while differences in opinion seem inevitable, a wide variety of
approaches are available for roadless area management. Roadless area
management, like all multiple-use land management, is fundamentally an
exercise in discretion and policy judgment concerning the best use of
the NFS lands and resources, informed by the underlying facts and
reasonable projections of possible social, economic, and environmental
consequences.
While the Tongass National Forest has endured debate regarding land
and natural resource management for decades, there are common
agreements. Tongass National Forest roadless areas are vast and
valuable. The Tongass National Forest contributes ecological values
locally, regionally, nationally, and internationally. Local communities
are reliant on or impacted by federal land management decisions, and
there is not always consensus, at the local level, on land management
priorities. All acknowledge that there are diverse opinions and views
concerning whether and how road construction and timber harvesting
should be restricted. To be sure, the USDA has received many comments
that highlight differences in views concerning factual matters and
methodologies, as well as general opinions and preferences. The USDA is
grateful for the attention and interest that communities, stakeholder
groups, and individuals have devoted to helping shape and improve the
FEIS for decision-making purposes.
Importantly, the final rule's change in policy does not
fundamentally rest on new factual findings contradicting the factual
findings the USDA made in its 2001 Roadless Rule. Rather, the policy
judgments implemented through this new rulemaking are ultimately the
result of assigning different value or weight to the various multiple
uses. Although many circumstances have changed since 2001, such as the
size and economic role of the timber industry in southeast Alaska, the
nature and role of southeast Alaska's roadless areas have not changed.
The currently-designated roadless areas continue to provide large
tracts of undeveloped land for roadless values, watershed protection,
and ecosystem health even while the Tongass National Forest was
exempted from the 2001 Roadless Rule from 2001 to 2011.
The FEIS carefully analyzes the environmental consequences of both
continued operation of and exemption from the 2001 Roadless Rule. That
analysis reveals only a modest difference in potential environmental
consequences between those (or any) alternatives. For example, although
9.4 million acres would no longer be subject to the 2001 Roadless Rule
with the final rule, only 186,000 more acres would become available for
timber production, and road construction is estimated to increase
Tongass-wide from 994 miles in the no-action alternative to 1,043 miles
in the final rule over the next 100 years. As many commenters have
pointed out, the results of this analysis are attributable to the fact
the 2001 Roadless Rule is not the primary limiting factor for Tongass
National Forest timber harvest, and that the level of timber harvest
defined in the Forest Plan has a greater influence. Similarly, the 2001
Roadless Rule would not seem to be the impediment to certain vital
infrastructure and energy projects as claimed by some, given that some
infrastructure and energy development is allowed under various statutes
and/or the 2001 Roadless Rule.
Under the current Administration, the USDA has refocused policies,
programs, and resources on increasing rural economic opportunity,
decreasing federal regulation, and streamlining federal government
services. The USDA concludes in light of the FEIS that a policy change
for the Tongass National Forest can be made without major adverse
impacts to the recreation, tourism, and fishing industries, while
providing benefits to the timber and mining industries, increasing
opportunities for community infrastructure, and eliminating unnecessary
regulations.
The Secretary of Agriculture has broad authority to protect and
administer the NFS through regulation as provided by the Organic
Administration Act of 1897 (Organic Act), the Multiple-Use Sustained
Yield Act of 1960, and the National Forest Management Act of 1976
(NFMA). These statutes provide the Secretary of Agriculture with
discretion to determine the proper uses within any area, including the
appropriate resource emphasis and mix of uses. In doing so, USDA
considers the relative values of the various resources and seeks to
provide for the harmonious and coordinated management of all resources
in the combination that will best meet the needs of the American
people. Roadless areas provide real and important values, such as high
quality or undisturbed soil, water and air; sources of public drinking
water; diversity of plant and animal communities; habitat for
threatened, endangered, proposed, candidate, and sensitive species;
primitive and semi-primitive classes of dispersed recreation; reference
landscapes; natural appearing landscapes with high scenic quality;
traditional cultural properties and sacred sites; and other locally
identified unique characteristics. However, roadless values are not the
only values that should be taken into consideration. The Organic Act
and Multiple-Use Sustained Yield Act mandate the Forest Service to
manage NFS lands for multiple uses and sustained yield of the various
renewable surface resources to meet the needs of the American people.
The State of Alaska's Citizens Advisory Committee devoted
considerable time and effort capturing the many and varied aspects of
roadless characteristics from an Alaska-specific viewpoint, and the
USDA is grateful for their dedication and insights. Similarly, tribal
government cooperating agencies expressed concern about removal of the
2001 Roadless Rule but expressed an interest in expanded regulatory
flexibility within their traditional territories. Here too, the USDA is
grateful for their participation as cooperating agencies and for the
knowledge and insights they have brought to the rulemaking.
Unquestionably, there are differences of perspective and opinion as
to how to best shape restrictions that protect a beloved resource while
providing cultural, social, and economic benefit for both local
communities and the nation, which is reflected in the 267,000 comments
received on the proposed
[[Page 68692]]
rule and DEIS (summarized in Appendix H of the FEIS). The USDA's
assessment is that the best mechanism to account for these many and
competing interests is to return the regulatory landscape back to what
it was prior to the promulgation of 2001 Roadless Rule and to allow
land management to be governed through the NFMA forest planning
process.
Alaska-Specific Statutes
The USDA has also considered several Alaska-specific statutes
applicable to the Tongass National Forest in selecting the final rule.
To be clear, all the alternatives considered are within the lawful
discretion of the USDA to select, and all would comply with applicable
statutes. No statute compels or prohibits establishment of any of the
various roadless rule alternatives; these alternatives would all be
within the USDA's discretion.
In assessing roadless management for these lands, the USDA has
considered the Alaska-specific legislation that Congress has enacted
during the past forty years, especially the TTRA and ANILCA.
Tongass Timber Reform Act
The TTRA directs the Forest Service to seek to provide a supply of
timber from the Tongass National Forest that meets annual market demand
and the market demand for each planning cycle to the extent consistent
with providing for the multiple-use and sustained-yield of all
renewable resources and other applicable requirements, including the
NFMA. The Tongass Forest Plan anticipates sufficient timber
availability to meet projected demand as described in the 2016 Forest
Plan FEIS and ROD. In addition, the Tongass Forest Plan provides
guidance to conduct annual monitoring and review of current timber
demand. Similarly, TTRA provides for protection of riparian habitats
and the multiple use and sustained yield of all renewable surface
resources.
Alaska National Interest Lands Conservation Act--Subsistence
Determination
ANILCA, as amended, contains several provisions that apply to
management of the Tongass National Forest. An ANILCA Section 810
evaluation and determination is not required to exempt the Tongass
National Forest from the 2001 Roadless Rule--a rulemaking process and
programmatic-level decision that is not a determination whether to
``withdraw, reserve, lease, or otherwise permit the use, occupancy, or
disposition'' of NFS lands. However, a forest-wide evaluation and
determination is included in this roadless area rulemaking to honor
regional commitments and inform future project-level planning and
decision-making subject to ANILCA Section 810 (16 U.S.C. 3120). An
ANILCA Section 810 subsistence analysis and determination was not
prepared when the 2001 Roadless Rule was promulgated.
The final rule has been evaluated for potential effects on
subsistence uses and needs in a manner consistent with Section 810 of
ANILCA. The FEIS discloses direct, indirect, and cumulative effects on
three subsistence use factors including: (1) Resource distribution and
abundance; (2) access to resources; and (3) competition for the use of
resources (Chapter 3, Subsistence). Importantly, the final rule does
not authorize ground-disturbing activities, but instead offers greater
flexibility in locating future road construction, road reconstruction,
and timber harvest activities. The Tongass Forest Plan will continue to
guide timber harvest and road construction, with the administrative
change prescribed in this rule only serving to conform and clarify the
lands available for timber harvest following the exemption from the
2001 Roadless Rule.
Consequently, total timber harvest volume will remain constant
across alternatives, and the risk of a significant restriction to
subsistence resource abundance and distribution is largely equivalent
across alternatives. The final rule may eventually influence
subsistence resource access due to timber management activities, but
these changes will be addressed on a site-specific basis, including
appropriate public engagement opportunities, as projects are proposed.
Competition for subsistence wildlife and seafood resources near
rural communities is affected by a variety of factors including
regulations, technology, wildlife distribution, modes of access, and
natural decreases in population. The final rule assumes new roads near
communities connected to other communities by ferry or road, combined
with increasing habitat reductions and consistent user demand, will
likely increase subsistence resource competition over time.
Based on the identified assumptions and analysis, the final rule
may eventually indirectly result in a significant restriction of
subsistence use of deer by increasing overall competition for the
subsistence resource by urban and rural residents. This finding is most
applicable to Chichagof, Baranof, and Prince of Wales Islands where
competition for deer and some other land mammals is already high and
habitat capacity has been significantly reduced due to prior timber
harvest and road construction activities. Notably, the predicted
restriction of subsistence use of deer due to increased competition in
the FEIS is substantially similar to Forest Plan subsistence effects
analysis because the Forest Plan will continue to guide total timber
harvest volume.
ANILCA subsistence hearings were conducted for the DEIS and
proposed rule, consistent with Section 810, by: (1) Giving notice to
the appropriate state agency, local committees, and regional councils;
and (2) giving notice of, and holding, ``a hearing in the vicinity of
the area involved.'' As the geographic area of interest is the entire
Tongass National Forest, subsistence hearings were conducted in 18
communities located across southeast Alaska to collect oral testimony
regarding the DEIS and associated subsistence resource and use
analysis.
Section 810 requires that when a use, occupancy, or disposition of
public lands may result in a significant subsistence use restriction, a
determination must be made whether: (A) Such a significant restriction
of subsistence uses is necessary, consistent with sound management
principles for the utilization of the public lands, (B) the proposed
activity will involve the minimal amount of public lands necessary to
accomplish the purposes of such use, occupancy, or other disposition,
and (C) reasonable steps will be taken to minimize adverse impacts upon
subsistence uses and resources resulting from such actions. Each of
these three points are discussed below.
Necessary, Consistent with Sound Management of Public Lands. The
final rule has been examined to determine whether the potential for a
significant restriction of subsistence uses is necessary, consistent
with the sound management of NFS lands. The final rule is designed to
provide a mix of resources and benefits to best meet the needs of the
American people. Some of the resource uses necessary to achieve these
benefits have the potential to adversely affect subsistence uses within
the Tongass National Forest. In light of the Forest Service's multiple-
use mandate and other requirements of law, the Forest Service has
determined that these effects to subsistence uses are necessary and
consistent with the sound management of NFS lands. (The Forest Service
again notes that making this determination is not required for purposes
of issuing this rule, but it is the Department's policy preference to
make this determination, and the other
[[Page 68693]]
determinations explained below related to ANILCA Section 810, on a
voluntary basis in light of the considerations noted above.)
Amount of Public Land Necessary to Accomplish the Purposes of the
Proposed Action. The land area evaluated through this rulemaking is the
Tongass National Forest and the IRAs therein. These lands constitute
the amount of land necessary to assess operation of the 2001 Roadless
Rule within the Tongass National Forest as requested by the State of
Alaska's petition. This rulemaking considered applying various
prohibitions and exceptions to different numbers of acres through the
development and analysis of a range of alternatives. The final rule,
however, removes the 2001 Roadless Rule's land classification system
and associated prohibitions and exceptions, and allows management to
return to operation under the Forest Plan. Accordingly, the final rule
addresses the amount of NFS land necessary to accomplish the proposed
action.
Reasonable Steps to Minimize Adverse Impacts to Subsistence Uses
and Resources. The continuation of subsistence opportunities, and
reasonable steps to minimize effects on subsistence resources, are
provided by Tongass Forest Plan forest-wide standards and guidelines
for subsistence, as well as related standards and guidelines for
riparian areas, fish, and wildlife. Many important subsistence areas
are assigned LUDs that exclude timber harvesting and road construction.
Beach and estuary fringe forest-wide standards and guidelines generally
apply to beach fringe and estuarine areas not under more restrictive
designations. Adverse impacts to subsistence resources and uses are
minimized through these measures. The potential site-specific effects
on subsistence uses, and reasonable ways to minimize these effects,
will be analyzed and considered during project-level design and
decision-making.
The final rule does not authorize ground-disturbing activities, but
instead offers greater flexibility in locating future development
activities on the Tongass National Forest. It is not possible to
substantially reduce timber harvest in some areas by concentrating it
in other areas without affecting subsistence resources and uses
important to other communities. Also, concentrating timber harvest
outside more important subsistence areas while still meeting Tongass
Forest Plan timber harvest goals could not be done without affecting
the natural distribution of wildlife species or without potential
significant effects to watersheds. These potential environmental
effects will be comprehensively studied and disclosed through the
future analysis of Tongass National Forest projects.
2001 Roadless Rule's Original Purpose
The USDA is mindful of the original stated purposes of the 2001
Roadless Rule in lifting the rule's restrictions for the Tongass
National Forest. The stated purposes of the 2001 Roadless Rule included
retention of the largest and most extensive tracts of undeveloped land
for the roadless values, watershed protection, and ecosystem health;
and fiscal considerations, mainly the cost of managing the road system
to safety and environmental standards. Specific to the Tongass, the
2001 Roadless Rule's Record of Decision noted that social and economic
considerations were key factors in analyzing alternatives, along with
the unique and sensitive ecological character of the Tongass National
Forest, the abundance of roadless areas where road construction and
reconstruction are limited, and the high degree of ecological health.
(66 FR 3254). The past 20 years of experience managing the Tongass
National Forest, with and without the rule in operation, provides an
important window for assessing whether the 2001 Roadless Rule's
prohibitions should be maintained.
From 2001 to 2011, the Tongass National Forest was exempt from the
2001 Roadless Rule. During this time, about 4,300 acres of IRAs were
entered for timber harvest and about 19 miles of roads were constructed
in association of that timber harvest. Of that only 300 acres of timber
harvest and 0.5 miles of road were authorized during the exemption
period and the remaining timber harvest and road construction were
authorized prior to the promulgation of the 2001 Roadless Rule. After
the harvest units and roads are buffered in GIS, this accounts for
about one percent of the substantially altered areas (roaded roadless
areas) removed from roadless designation in Alternatives 2 through 5.
The remaining 99 percent of the roaded roadless areas are from mapping
errors and activities that occurred before 2001 (36%) or were allowed
under the 2001 Roadless Rule (62%).
A significant percentage of the Tongass National Forest remains
undeveloped, providing for large, extensive tracts of undeveloped land,
but much of that is characterized as rock, ice, or muskeg. The final
rule will make an additional 188,000 forested acres available for
timber harvest with the majority characterized as old-growth timber.
The young-growth transition strategy as described in the 2016 Tongass
Forest Plan ROD outlines a glide path to decrease old-growth harvest
annually on the Tongass until it reaches about 5 million board feet
(MMBF) harvest per year, expected to occur in about 2032. After the
young-growth transition is fully implemented, it is unlikely that a
significant portion of the areas previously designated as IRAs would be
considered for harvest because the focus for timber harvesting will
shift to the previously roaded, young-growth areas.
Watershed protection was a prominent aspect in the decision to
adopt the nationwide 2001 Roadless Rule. Looking at the Tongass
National Forest today, watershed protection goals are well provided for
even without the current roadless rule. Large tracts of undeveloped
lands and watershed protections are provided by existing statutory and
forest plan direction, including lands in designated Wildernesses and
National Monuments. In addition, the TTRA (Pub. L. 101-626, Title II,
Section 201) and the National Defense Authorization Act for Fiscal Year
2015 (Pub. L. 113-291, 128 Stat. 3729, Section 3720(f)) designated
approximately 856,000 acres as LUD II areas, which are managed in a
roadless state to retain their wildland character. Approximately 3.6
million acres in key watersheds (defined in the Forest Plan as Tongass
77 Watersheds and The Nature Conservancy/Audubon Conservation Areas)
are managed for no old-growth timber harvest, thus minimizing adverse
impacts to fisheries. Management direction of LUD II areas and key
watersheds would remain unaffected with the final rule.
Ecosystem health was another important element of the 2001
rulemaking. Once again, the FEIS reveals only a moderate difference
between implementation of the 2001 Roadless Rule and the final rule. A
key indicator of ecosystem health for the Tongass National Forest is a
functional and interconnected old-growth ecosystem. Under the final
rule, long-term protection of productive old growth would continue to
occur under the Forest Plan's old-growth habitat conservation strategy.
Connectivity between old-growth reserves would continue to be
maintained through Forest Plan direction for stream buffers, the beach
and estuary fringe, and legacy forest structure. Under the final rule,
the projected amount of old-growth harvest and percent of original
productive old-growth remaining over the next 100 years would remain
unchanged from
[[Page 68694]]
implementation of the 2001 Roadless Rule (Alternative 1--No Action).
Although it may seem counter-intuitive that eliminating the 2001
Roadless Rule's timber harvest restrictions across 9.3 million acres
would not increase old-growth timber harvest, timber harvest levels are
controlled to a far greater extent by other factors, primarily economic
factors. Additionally, the Forest Plan's young-growth transition
strategy will transition harvest locations away from roadless areas
containing old growth and into areas where timber harvest has
previously occurred, avoiding or reducing effects to roadless areas.
The underlying economic considerations and the young-growth transition
strategy are far greater influences than the 2001 Roadless Rule. This
strategy will remain in place, with or without the 2001 Roadless Rule.
Limited road maintenance budgets were another factor cited in
support of the 2001 Roadless Rule. The 2001 Roadless Rule cited fiscal
concerns over building new roads in IRAs due to an $8.4 billion backlog
of deferred maintenance across the NFS transportation system at that
time. Recent deferred maintenance records were reviewed; a sound
comparison could not be made with the deferred maintenance levels of
2001, due to substantial changes in defining and interpreting deferred
maintenance. Since 2001, the inventory methods and roads considered to
be part of deferred maintenance have changed multiple times (2002,
2005, 2007, 2012, and 2013). These changes make a direct comparison
with 2001 deferred maintenance numbers impracticable.
The FEIS projects that about 1,043 miles of new road construction
could occur over the next 100 years across the Tongass National Forest,
mainly to support timber harvest operations, as compared with the
approximately 994 miles of new roads projected forest-wide over the
next 100 years under Alternative 1--No Action. The 994 miles of new
road construction projected for Alternative 1 are outside of
inventoried roadless areas. The final rule is not expected to
materially increase the amount of timber harvested in the Tongass, as
that is prescribed and managed by the Forest Plan. However, the final
rule does impact the location from which the timber may be harvested,
by allowing access to areas that were off limits under the 2001
Roadless Rule.
National Versus Local Decision-Making
For decades, the USDA has worked with states, tribes, local
communities and collaborative groups toward land management solutions
for roadless areas. Sometimes solutions have been found nationally.
Sometimes a state-by-state approach has been the best option. Often,
the solutions are found forest-by-forest or even area-by-area. In this
instance, the national rule's one-size-fits-all approach to roadless
area management is not the best approach for roadless area management
on the Tongass National Forest. Other states, Idaho and Colorado, have
sought and been granted the opportunity for roadless management to be
tailored to their needs. Indeed, the USDA received at least thirteen
individual state petitions seeking various state-specific solutions
during the timeframe in which the 2001 Rule had been judicially
invalidated. The State of Alaska's 2018 rulemaking petition implores
the USDA to recognize that in contrast to the scarcity of undeveloped
lands that occurs in many other states, undeveloped areas are plentiful
in Alaska. Instead, the State of Alaska maintains that the
circumstances of the Tongass National Forest appear to be best managed
through the local planning processes. The Forest Service's 40 years of
experience with forest planning under NFMA, which includes forest plans
subject to periodic review and adjustment, routinely demonstrates the
planning system's capacity to account for both local and national
interests and provide durable and widely accepted solutions providing
for the multiple use and sustained yield of the many goods and services
provided by the NFS.
The final rule would leave the roadless area management issue open
for future consideration in the forest planning process. The forest
planning process is more flexible than the 2001 Roadless Rule's
regulatory approach, because plans are expected to be designed and
attuned to local circumstances and are intended to be periodically
reviewed. The 2001 Rule's prescriptive approach forecloses a full
balancing of interests during future forest planning processes. The
final rule will allow local decision makers the flexibility to address
roadless management based on changed local conditions, new unforeseen
issues, and take into account state and local economic development
plans. In addition, the final rule will provide local discretion during
future forest planning efforts to explore roadless area management
alternatives, unconstrained by the 2001 Roadless Rule, with local
stakeholders, communities, and tribal governments.
In selecting the final rule among the several alternatives
considered, the USDA has given substantial weight to the State of
Alaska's policy preferences as expressed in its Petition. The State of
Alaska's preference to emphasize rural economic development
opportunities is consistent with the findings of the Interagency Task
Force on Agriculture and Rural Prosperity established by Executive
Order 13790 issued April 25, 2017.\1\ The USDA recognizes that ensuring
rural Americans can achieve a high quality of life is one of the
foundations of prosperity.\2\ The State of Alaska's views on how to
balance economic development and environmental protection offer
valuable insight when making management decisions concerning NFS lands
within Alaska.
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\1\ See Report to the President of the United States from the
Task Force on Agriculture and Rural Prosperity (Oct. 21, 2017),
https://www.usda.gov/sites/default/files/documents/rural-prosperity-report.pdf).
\2\ See id. at 2, 21-25; see also id. at 26-29, 35-42 (calls to
action for supporting a rural workforce and developing the rural
economy).
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Southeast Alaska's rural communities have relied upon the Tongass
for important natural resources and environmental opportunities
supporting recreation, fishing, and the timber industries. In
particular, the timber industry has historically played an important
economic role in southeast Alaska's rural economy providing jobs in
small and remote communities with high unemployment rates and limited
employment opportunities. In these isolated communities, every job has
impacts at household and community levels. Notably, the timber industry
has faced sustained hardship during the past two decades, with rural
communities suffering the socioeconomic consequences. The final rule
will increase the number of acres available for timber harvest acres
and improve overall flexibility in locating timber sales. In turn, this
would provide additional opportunity for the struggling timber industry
and support rural communities with limited employment opportunities
without increasing the amount of overall timber harvested. USDA and the
State of Alaska believe both roadless area conservation and other
multiple-use values with important local socioeconomic consequences are
meaningfully addressed through local and regional forest planning on
the Tongass National Forest without 2001 Roadless Rule prohibitions on
timber harvest and road construction/reconstruction.
The USDA recognizes that the majority of Alaska Native tribes and
[[Page 68695]]
local communities throughout southeast Alaska support keeping the 2001
Roadless Rule in place, as expressed in the multitude of resolutions
and comment letters received during the 60-day comment period. USDA
appreciates that not all local communities share the State of Alaska's
views and has carefully considered the views and preferences provided
by all the leaders and citizens that have participated through various
public meetings and comment periods. The USDA urges those groups and
individuals to regularly engage with the Tongass National Forest and
Forest Service Alaska Region concerning forest planning efforts and
project design. The lifting of the 2001 Roadless Rule on the Tongass
National Forest in no way impedes citizen participation; rather, it
affords interested parties the opportunity to work with the Forest
Service to seek more efficient solutions that account for all
interests.
Relationship of the Alaska Roadless Rule to the Forest Plan
The NFMA requires the Forest Service to develop, maintain and, as
appropriate, revise land and resource management plans for units of the
NFS. Land management plans provide a framework for integrated resource
management and for guiding project and activity decision-making, but
plans do not authorize projects or activities or commit the Forest
Service to take action. A revised Tongass Forest Plan was issued in
1997 and amended in 2008 and 2016. Forest planning is a distinct and
separate process from USDA's various roadless rulemakings.\3\ Excluding
the Tongass from the 2001 Roadless Rule's prohibitions returns
management discretion to the Agency's standard planning process. The
existing Forest Plan provides adequate direction and protection of
roadless characteristics such that retention of the 2001 Roadless Rule
is not required. Future plan revisions will assure roadless
characteristics are periodically assessed and management direction can
be adjusted if warranted (increased, decreased or blended differently)
in order to account for the best multiple use management possible.
---------------------------------------------------------------------------
\3\ See Kootenai Tribe of Idaho v. Veneman, 313 F. 3d 1094, 1117
n.20 (9th Cir. 2002), abrogated on other grounds by Wilderness
Society v. USFS, 630 F.3d 1173 (9th Cir. 2011); and Wyoming v. USDA,
661 F.3d 1209, 1269-72 (10th Cir. 2011).
---------------------------------------------------------------------------
All forest plans must conform to existing laws and regulations as
well as new laws and regulations. See 36 CFR 219.1(f) and 219.13(c).
The USDA's previous roadless rules, national and state-specific, have
directed that: (1) No amendment or revision of any forest plan was
compelled by promulgation of such rules; (2) subsequent forest planning
decisions could not revise the Secretary's regulatory instructions; and
(3) line officers were to conform project decisions to the prohibitions
and exceptions set forth in the applicable rules. The final rule
continues this approach, with one exception necessitated by a single
element of the 2016 Tongass Forest Plan Amendment.
The final rule directs the Tongass Forest Supervisor to issue a
ministerial Notice of Administrative Change pursuant to 36 CFR
219.13(c) identifying plan changes made in conformance with the
regulatory determinations of this subpart; specifically the rescission
of the portion of the December 9, 2016, ROD concerning suitable timber
lands attributed exclusively to implementation of the January 12, 2001,
Roadless Area Conservation Rule (66 FR 3244). This administrative
change is appropriate because the Region took the step in 2016 of
amending the Tongass Forest Plan to directly implement the 2001
Roadless Rule's timber harvesting prohibitions despite the 2001
Roadless Rule's express admonition that it did not compel the amendment
or revision of any land and resource management plan. See 2016 Tongass
Forest Plan, Appendix A, page A-3, Appendix I, page I-177 (indicating
all IRA were removed from the suitable land base during Stage 1 of the
suitability analysis due to the 2001 Roadless Rule) and 36 CFR
294.14(b) (directing that the 2001 Rule does not compel the amendment
or revision of any land and resource management plan). The 2016 Forest
Plan sought to directly implement the 2001 Roadless Rule prohibitions
via the timber suitability analysis. Today's decision to rescind the
2001 rule's prohibition as to the Tongass National Forest makes the
2016 Amendment's effort to implement the 2001 rule's prohibitions
obsolete. Because allowing the inconsistent portion of the 2016
suitability designations to stand would effectively nullify the
Department's regulatory choice to remove the 2001 timber harvest
prohibitions, the final regulation gives an express regulatory
instruction to conform the plan to the new regulatory regime. As
explained in greater detail below, there is no requirement or credible
justification that warrants undertaking additional planning efforts
above and beyond the administrative change directed by this rulemaking.
The administrative change simply provides conformance of the Forest
Plan with the final rule in regard to lands suitable for timber
production and does not change the level of timber harvest, how timber
is harvested on the Tongass, or any other aspects of the Forest Plan.
As previously noted, forest planning is a distinct and separate
process from USDA's various roadless rulemakings. The referenced 2001
Roadless Rule's scope and applicability language was designed to avoid
conflicts between itself and forest plans, as well as avoiding
unnecessary or duplicative administrative processes for the operation
of the 2001 Roadless Rule. Just as it was unnecessary to immediately
install the 2001 Roadless Rule's higher order prohibitions through
individual plan amendments, it is unnecessary here to duplicate these
rulemaking efforts through a separate plan amendment. Fortunately, the
2012 NFMA planning regulations (36 CFR 219.13(c)) make provision for
instances where overriding statutes or regulations change. The planning
regulations direct that plans may be adjusted via notice of
administrative change without resorting to the standard plan amendment
process. The USDA is empowered to prescribe such regulations as it
determines necessary and desirable to carry out the planning process
(16 U.S.C. 1613) as well as to redeem and reconcile its regulations
governing overall multiple use management responsibilities, including
roadless matters.
To promote clarity, transition language has been added to the final
rule. The language is similar as was set out for the other action
alternatives in the DEIS. The operational result will be that 188,000
acres will be returned to the suitable timber base via the
administrative change provision of the planning regulations (36 CFR
219.13(c)). The revised transition language assures that all other
aspects of the Tongass Forest Plan remain operational under the rule
including the goals, objectives, management prescriptions, standards,
guidelines, projected timber sale quantity, projected wood sale
quantity, and the young-growth transition strategy. This includes
direction for non-timber resources including riparian management
standards and guidelines, which provide protection for fisheries with
subsistence and commercial importance. Any timber harvest, including
any timber harvesting in areas formerly designated as IRAs, would be
compelled to adhere to these resource standards and guidelines
including fish habitat, water quality, air, recreation, and other
resources. Consistency with Forest Plan direction continues under all
alternatives.
[[Page 68696]]
Although the Forest Service has broad discretion to amend or revise
forest plans management direction, any change would need to be
consistent with applicable law, regulation, and policies. Any future
forest plan amendments or revisions would include a public involvement
process pursuant to the Agency's planning regulations and NEPA.
Public Comment Process
The Forest Service published an NOI to prepare an EIS for the
Alaska Roadless Rule in the Federal Register (83 FR 44252) on August
30, 2018. The NOI initiated a 45-day scoping period which ended on
October 15, 2018. During this time period, the Forest Service conducted
17 public meetings including meetings in Anchorage, AK; Washington, DC;
and communities throughout southeast AK: Angoon, Craig, Gustavus,
Hoonah, Kake, Ketchikan, Petersburg, Point Baker, Sitka, Tenakee
Springs, Thorne Bay, Wrangell, Yakutat, and two meetings in Juneau.
During the scoping period, just over 144,000 comment letters or emails
were received.
On October 17, 2019, the Department published a notice of proposed
rulemaking in the Federal Register (84 FR 55522) and on October 18,
2019, an NOA for the DEIS was published (84 FR 55952). On October 25,
2019 an amended NOA was published (84 FR 57417) which amended the
comment closing date of the 60-day comment period to December 17, 2019.
During the 60-day comment period, the Forest Service conducted 21
public meetings including Anchorage, Alaska; Washington, DC; and
southeast Alaska communities: Angoon, Craig, Gustavus, Haines, Hoonah,
Hydaburg, Juneau, Kake, Kasaan, Ketchikan, Pelican, Petersburg, Point
Baker, Sitka, Skagway, Tenakee Springs, Thorne Bay, Wrangell, and
Yakutat. Approximately 267,000 comment letters or emails were received
during the 60-day comment period, including 11 petitions containing
about 117,000 signatures.
Cooperating Agencies
On July 30, 2018, the Forest Service invited 32 Alaska federally
recognized tribes to participate as cooperating agencies during the
rulemaking process. Originally six tribes agreed to become cooperating
agencies including Angoon Community Association, Central Council
Tlingit and Haida Indian Tribes of Alaska, Hoonah Indian Association,
Hydaburg Cooperative Association, Organized Village of Kake, and
Organized Village of Kasaan. After the publication of the proposed rule
(October 17, 2019), the Organized Village of Kake withdrew as a
cooperating agency. After the publication of the FEIS (September 25,
2020), the remaining tribal cooperating agencies, Angoon Community
Association, Central Council Tlingit and Haida Indian Tribes of Alaska,
Hoonah Indian Association, Hydaburg Cooperative Association, and
Organized Village of Kasaan withdrew as cooperating agencies.
The State of Alaska agreed to become a cooperating agency on August
2, 2018. Cooperating agencies participated throughout the rulemaking,
providing their knowledge and expertise to design alternatives, analyze
alternatives, and refine the analysis set out in the DEIS and FEIS.
The Forest Service made several trips to several of the villages to
work individually with tribal cooperators, provide technical expertise,
and collect input. All tribal cooperators opposed the proposed rule
(Alternative 6), however, were supportive of additional local control,
increased opportunity for local forest product businesses, and limited
increased access for a variety of local needs.
Based on input from tribal cooperating agencies, USDA considered
the use of the Alaska Native tribes' traditional use areas for the
community use analysis boundaries in the development of the DEIS. USDA
did not utilize the traditional use areas for the impact analysis
because they are considerably larger than the community use areas. The
use of larger analysis areas diffuses the impacts and the Agency wanted
the impacts to be focused by community. The Agency added an appendix
displaying the traditional use areas to recognize the importance of the
traditional use areas to the Alaska Native tribes.
The Agency revisited the analysis boundary issue between the DEIS
and FEIS, and solicited subsistence use data by community from the
State of Alaska. Alaska Department of Fish and Game provided updated
survey information from six communities regarding areas of subsistence
gathering. Data indicate southeast Alaskans are traveling further for
subsistence gathering, meaning the community use areas are larger.
Again, the larger area would diffuse the impacts. The agency determined
this would not be an improvement to the impact analysis and would make
it more difficult for readers to determine the impacts.
The USDA appreciates and recognizes the contributions of the five
Alaska Native tribes who withdrew as cooperating agencies on October
13, 2020. The USDA understands that the final rule is not the outcome
the tribal cooperating agencies had hoped for, and the Department
recognizes the concerns they expressed. The Department and Forest
Service greatly value each tribal cooperating agency. The participation
and advice of tribal cooperating agencies improved the analyses and
alternatives. The Department's hope is that removal of the 2001
Roadless Rule's blanket prohibitions will create space for more
creative solutions that are sensitive to the diverse interests of
Alaskan Native Tribal communities. As the tribal cooperating agencies'
withdrawal letter eloquently suggests, the Department too desires to
invest in solutions that will tend the land and serve the people.
Comments on the Proposed Rule
Approximately 267,000 comments were received on the proposed rule
and DEIS, including 11 petitions containing about 117,000 signatures,
during the 60-day comment period. A large majority of written comments
and oral subsistence testimony supported retaining the 2001 Roadless
Rule on the Tongass National Forest. Notably, a significant proportion
of the 267,000 comments letters were from outside Alaska. A significant
proportion of southeast Alaska municipal and tribal governments
submitted resolutions supporting the 2001 Roadless Rule's application
on the Tongass National Forest. However, many of the State's elected
officials, including the Governor, the federal delegation, and some
municipal governments support changing the 2001 Roadless Rule. The USDA
considered all substantive comments as part of the rulemaking,
including testimony given at the subsistence hearings. The following is
a summary of the comments received relating the final rule and the
agency response. A full detailed response to comments is contained in
Appendix H of the FEIS.
Sec. 294.50 Tongass National Forest. No substantive comments were
received in regard to the rule language for this section. Therefore, no
changes were made to this section.
Sec. 294.51 Chugach National Forest. Comments were received
expressing concerns regarding the proposed administrative correction
and boundary modification provisions for the Chugach National Forest.
Commenters and cooperating agencies were concerned that the proposed
provisions were too broad and could be used by the Forest Service to
open significant portions of the Chugach to additional logging.
Based on the experience of implementing the 2001 Roadless Rule,
[[Page 68697]]
boundary modifications are sometimes needed to account for errors,
better mapping technology, land exchanges, etc. Thus, the two state-
specific roadless rules, Idaho and Colorado, have administrative
correction and modification provisions (36 CFR 294.27 for Idaho and 36
CFR 294.47 for Colorado) that operate differently than the 2001
Roadless Rule. The intent of the administrative correction and
modification provisions for Alternatives 2 through 5 was to align
processes and install a single system for the two National Forests of
Alaska. However, some members of the public expressed alarm that the
provision could be used to entirely undo roadless protections on the
Chugach National Forest. This was never USDA's intent. While alignment
of administrative procedures between all state-specific roadless rules
might have offered some administrative efficiencies for managing
roadless boundaries nation-wide, the final rule gains some
administrative efficiencies by fully removing roadless rule provisions
for the Tongass National Forest.
Section 294.51 has since been retitled as ``Transition,'' and now
includes the instruction to the Tongass Forest supervisor to issue an
administrative change in regard to the lands suitable for timber
production. This provision was inadvertently not included in the
Alternative 6 rule language but was included in Alternatives 2 through
5 rule language and noted in the DEIS as applying to the final rule.
Comments regarding perceived impropriety associated with the
State's petition. Commenters expressed concern that the State developed
the petition and the Secretary accepted the petition without public
involvement, and that the petition was motivated by politics and
outdated timber economics.
The APA and USDA's implementing regulation (7 CFR 1.28) allows any
interested person to petition the Secretary to change a regulation.
There is no prescribed process for developing or responding to a
petition other than that it must be given prompt consideration and the
petitioner will be notified promptly of the disposition made of their
petition. The Secretary has no control over the underlying motivations
or data offered in support of a petition. However, once a petition is
accepted, a rulemaking in response to a petition will be conducted in
compliance with applicable law and regulations. The USDA has conducted
this rulemaking in compliance with all applicable law and carefully
considered the information provided by all those who participated in
the various public meetings and comment periods. The Department has
drawn its own conclusions based on the information provided by all
parties and its own analysis.
Comments on sufficiency of public outreach and involvement.
Commenters raised concerns regarding whether the length of comment
periods and the quantity and locations of public meetings were
sufficient.
The Forest Service conducted two cycles of public comment: the
first was a 45-day scoping period from August 30, 2018, to October 15,
2018, in which about 144,000 comment letters were received; and the
second was a 60-day comment period on the proposed rule and DEIS from
October 18, 2019, to December 17, 2019, which resulted in about 267,000
comment letters. During the scoping period 17 public meetings were held
and during the comment period 21 public meetings were held throughout
southeast AK, Anchorage, AK, and Washington, DC. The USDA recognizes
that many would have desired long scoping and comment periods. The
length of the scoping and comment periods are standard for both the
rulemaking and EIS processes. The robust meeting attendance and the
411,000 total comments received indicates the timing and length were
clearly adequate for many.
Comments on consideration of public input. Commenters were
concerned that input from the public was ignored because a large
majority of comments supported retaining the 2001 Roadless Rule and
opposed the full exemption, which was identified as the proposed rule
and preferred alternative.
The USDA values the comments received, and the concerns expressed
during the rulemaking process. The USDA considered public comments
received, the range of alternatives examined in the DEIS and FEIS, and
input from cooperating agencies and elected officials. Public comments
were utilized to craft the range of alternatives examined in the DEIS
and FEIS, modify the alternatives between DEIS and FEIS, and modify
analyses. The NEPA and rulemaking public comment process are not vote-
counting processes. Every comment has value, whether expressed by one
individual or thousands. The public comment process considers the
substance of each individual comment rather than the number received.
No interest group's views or comments are given preferential treatment
or consideration, and comments are considered without regard to their
origin, commenter's affiliation, or number received. Based on the
comments received, the Secretary reconsidered all alternatives and has
opted for alternative 6, the full exemption alternative.
Comments on tribal government-to-government consultation.
Commenters expressed concern that tribal consultation was inadequate.
In 2018, the Forest Service sent letters to the 32 federally
recognized tribes and 27 Alaska Native corporations in southeast and
southcentral Alaska to invite government-to-government and government-
to-corporation consultation. The in-region consultation invitation was
continuous throughout the rulemaking process.
The Alaska Region and the Tongass National Forest have an ongoing
government-to-government relationship with all federally recognized
tribes in southeast Alaska. The agency will continue to meet its
responsibility to consult with federally recognized tribes and Alaska
Native corporations through government-to-government and government-to-
corporation consultation on all topics. In addition to district
rangers, Regional Office staff also met with tribes, tribal
cooperators, and other interested parties to answer questions and
provide information as requested when feasible. Forest and Regional
Office staff provided briefings, information meetings, supported formal
consultations, and formal public hearings in or within the vicinity of
communities throughout southeast Alaska. Most tribal governments took
advantage of these opportunities. To date, twelve government-to-
government consultations have occurred in association with this
rulemaking effort.
Comments on the State's Citizen Advisory Committee. Commenters
expressed concerns regarding the composition and role of the committee
in the rulemaking process, whether the committee had undue influence,
and whether their involvement violated the Federal Advisory Committee
Act (FACA).
The committee was established by the State of Alaska under an
Administrative Order issued by Governor Walker in September 2018. The
committee was charged with providing recommendations to assist the
State of Alaska in fulfilling its role as a cooperating agency. The
thirteen committee members were selected by Governor Walker, and the
USDA and Forest Service had no part in the selection. The Forest
Service provided an individual to participate on the committee as a
non-voting member to provide procedural and technical information to
the committee.
The committee does not meet the definition of an advisory committee
as
[[Page 68698]]
defined by the FACA implementing regulations at 41 CFR 102-3.25. The
committee was established under state law by the Governor of Alaska.
The committee reported directly to the Governor who submitted the
committee's report to the USDA as part of the State's participation as
a cooperating agency. Intergovernmental coordination with the Governor
or his appointees is not subject to FACA. In any event, the USDA and
Forest Service did not manage or control the committee's operation and
did not utilize its work within the meaning of FACA. USDA's involvement
with the committee was limited to non-voting participation, providing
technical assistance. The committee did not have undue influence over
the rulemaking process.
Comments on support to the State of Alaska. Commenters expressed
concern that granting funds to the State of Alaska to support the
State's involvement in the Alaska roadless rulemaking process was a
misuse of congressional appropriations.
The agency provided the State of Alaska's Forestry Division with $2
million from the fiscal year 2018 Consolidated Program Grant (CPG),
Modification 2, utilizing the State Fire Assistance budget line item as
the source code. The modification discussed the specific use of the
funding, which could be used for: convening and facilitating a group
with a diverse mix of state-specific interests to inform the State's
input as a cooperating agency, public meetings, cooperating agency
support, economic analysis and planning, and to coordinate the proposed
state rule with existing land management planning efforts in progress
within the State of Alaska. A subsequent modification has been executed
utilizing $1.3 million of the funding to undertake wildland fire risk
reduction projects in several Alaska communities, primarily
construction of fuel breaks and maintenance of established fuel breaks.
USDA Office of the Inspector General has been asked to investigate this
matter and the agency is cooperating with the investigation.
Comments on the need to change from the 2001 Roadless Rule.
Commenters highlight that the DEIS projects minimal benefit for the
forest products industry and thus contend that the analysis does not
support the conclusion that eliminating the roadless rule will support
rural economic development. In addition, commenters questioned any need
for change and rationale in the Notice of Proposed Rulemaking to
support a change.
USDA's approach to rural economic development is a long-term multi-
faceted strategy outlined in the Report to the President of the United
States from the Task Force on Agriculture and Rural Prosperity (October
21, 2017), which includes regulatory reform, increasing the production
of natural resources, modernizing rural utilities, and improving
transportation infrastructure. The final rule reduces the regulatory
barrier to achieving these aspects of USDA's strategy for rural
economic development. Although there is only a minimal benefit from the
final rule to the forest products industry at this time, small
incremental change can help achieve rural prosperity over the long-
term. The final rule is a step in the right direction for rural
prosperity.
Comments on a local approach for roadless management. Commenters
questioned the proposed rule's assertion that the Tongass should be
managed locally suggesting it ignores the Forest Service's 2001
conclusion that national rulemaking was needed to protect roadless
areas.
As noted above, the unique circumstances of the Tongass National
Forest have been recognized and assessed since the 2001 rulemaking.
Then, as now, inclusion of the Tongass National Forest under the
national rule was not mandatory but represented a policy choice, as did
the national rule itself. In 2001 the Department eventually opted for
inclusion of the Tongass National Forest. In 2008 and 2012, two other
states requested and were granted the opportunity to discontinue
operation under the national rule. Today, the USDA concludes that the
interests furthered by the national rule are not improperly undone by
exempting a single forest that is now, and will remain for the
foreseeable future, substantially undeveloped and roadless. The
estimate of 49 miles of additional road construction (from 994 to
1,043) spread across 9 million acres of land, over the next 100 years,
will not undo the national rule's underlying goal of protecting
roadless area characteristics within the NFS, and moreover are well
within the USDA's discretion to further in light of the mix of mandates
and policy discretion embodied in the relevant governing statutory
provisions.
Comments on the administrative change procedure. Commenters were
concerned with the administrative change instruction for the lands
suitable for timber production in the Forest Plan, alleging it is
inconsistent with the National Forest System Land Management Planning
regulations at 36 CFR part 219 (2012 Planning Rule) and would require
an amendment. In addition, commenters were concerned that the agency
did not include this aspect of the rule during scoping.
The administrative change provision at 36 CFR 219.13(c) clearly
states that an administrative change includes changes to conform to new
regulatory requirements. Although the provision was not expressly
included in the proposed action during scoping, it was highlighted in
the DEIS and conforms to the requirements of the NEPA implementing
regulations.
Comments on subsistence mitigation. Commenters allege that the
Forest Service violated ANILCA and NEPA by refusing to consider
updating the roadless inventory to include lands important to the
Organized Village of Kake, mitigation measures proposed by Kake, and
allowing a greater management role for Kake in their traditional
territory.
The roadless inventories were updated and additional areas were
included in Alternatives 2 and 3 as designated Alaska Roadless Areas.
All unroaded areas were reviewed and some areas identified in the 2003
and 2008 roadless analyses associated with Tongass forest planning
efforts were included. In addition, small islands previously excluded
from roadless designation were included if not substantially altered.
Mitigation measures such as identifying specific road segments,
selling carbon credits, and workforce development are outside the scope
of the Alaska roadless rulemaking, which is programmatic and does not
evaluate projects or partnerships.
Co-management of the Tongass National Forest with tribal partners
was considered as an alternative but eliminated from detailed analysis
as it does not comport with existing legal authorities.
Comments on the site-specificity and qualitative nature of the
impact analyses. The analyses in the FEIS are a generalized review
which the Council on Environmental Quality recognizes as appropriate
for any broad or high-level NEPA review of proposed policies, plans,
programs, or projects. It is reasonable and efficient to limit detailed
site-specific impact analyses to when specific proposals are brought
before the agency. Locations of potential timber harvest and road
construction are not known at this time. While locations of other
developments, such as a regional energy or transportation project, may
be more predictable based on published information, it is not known if,
when, or specifically where they would occur. When specific timber
harvest or other
[[Page 68699]]
projects are proposed, site-specific NEPA analysis and required pubic
involvement would be conducted at that time. No on-the-ground actions
are authorized by the final rule.
Comments on the adequacy of the impact analyses. Commenters
variously questioned the adequacy of the impact analyses, disagreed
with the conclusions made, and contended that the effects are
understated. Commenters noted the obvious impacts of past timber
harvesting and road construction as evidence the impacts were
understated. In addition, commenters noted that the basis of the 2001
Roadless Rule was the recognition that timber harvesting and road
construction were impactful to roadless area values and
characteristics.
USDA does not dispute that timber harvesting and road construction
impact roadless area values and characteristics. However, the impact
analyses in the Rulemaking for Alaska Roadless Areas DEIS and FEIS do
not analyze the effects of harvesting timber and constructing roads in
a specific roadless area. Rather, the DEIS and FEIS analyze the
difference in effects under the 2001 Roadless Rule, the current Tongass
Forest Plan, and the other action alternatives. The baseline for
comparison of alternatives is not a pristine wilderness. Rather it is
the continuation or adjustment of current management. Under the 2001
Roadless Rule and Tongass Forest Plan, the Forest Service projects the
harvest of about 46 MMBF of timber per year across 227,000 available
acres of old-growth and 334,000 available acres of young-growth lands
with about 994 miles of new road construction across the 100-year
analysis period. Under the final rule (Alternative 6) the agency
projects the harvest of about 46 MMBF of timber per year across 395,000
available acres of old-growth and 354,000 available acres of young-
growth lands with about 1,043 miles of new road construction across the
100-year analysis period.
In addition, the impact analyses considered the continuation of the
young-growth transition strategy in all alternatives analyzed,
including the no-action alternative and the final rule alternative. The
young-growth transition strategy defines a 16-year period starting in
2016 in which the old-growth contribution to the projected timber sale
quantity decreases over time as young-growth matures and becomes more
economical to harvest. At year 16, the old-growth contribution to the
projected timber sale quantity would stabilize at 5 MMBF per year. The
young-growth transition strategy has a large beneficial environmental
effect on roadless areas because it shifts the focus of the Tongass
timber sale program to young-growth areas which are largely already
roaded. In addition, the smaller contribution of old-growth to the
projected timber sale quantity makes roadless areas less economical
because there are fewer acres of old-growth to off-set the high cost of
road construction in the Tongass National Forest. Old-growth is
generally more profitable than young-growth to harvest due to higher
volume per acre and the higher value of the larger trees. The impact
analyses in the FEIS is reflective of the small change between the
baseline and the action alternatives, and the impact of the young-
growth transition strategy.
Comments on cost-benefit analysis. Commenters expressed concern
about the cost-benefit analysis using changes in suitable old-growth
and young-growth acres as an indicator for potential displacement of
recreationists interested in primitive recreation experiences.
Primitive recreation is a class of recreation utilized to describe and
manage recreation opportunities. Primitive recreation opportunities
occur more than 3 miles from a road or motorized trail; in areas
generally greater than 5,000 acres; where social setting provide for
less than 6 party encounters on a trail; and are non-motorized,
typically include hiking, horse packing, fishing, hunting, and camping.
There was concern about the methodology used to measure adverse visitor
impacts. Commenters sought consideration of scenic values in the cost-
benefit analysis. Commenters also sought a cost-benefit economic
analysis that uses best available science to assess socioeconomic
impacts of each alternative as well as analysis of the socioeconomic
value and impact on fisheries, ecotourism, special use permits,
recreation, game populations, and subsistence resources. Other
commenters expressed concern about the inclusion of harvesting costs
(felling, yarding, and loading) and recreation expenditures, as a
distributional impact, in the cost-benefit analysis.
In response to public comment, the analysis of recreation
visitation related displacement and associated expenditures, in the
Regulatory Impact Analysis (RIA), has been updated based on new
information received during proposed and final rule preparation. Scenic
values, game species, and subsistence are discussed qualitatively in
the RIA and examined in more detail in the EIS. A cost-benefit analysis
has also been included in the RIA with new data and information
received during proposed and final rule preparation. This analysis
includes benefits from a more efficiently managed timber sale program
alongside agency costs, forgone conservation value, and costs of
potentially displaced recreationists. The revised RIA includes
discussion and analysis of costs from felling, yarding, and loading
timber and acknowledges their limited scope alongside other costs to
the timber industry and costs to the agency from road maintenance. In
addition, detail has been added to the RIA, noting that road cost
changes before and after 2011 were twice as high during the exemption,
and the relevance of these costs alongside haul cost savings. Potential
recreation related revenue losses can be considered distributional if
there are substitute opportunities in southeast Alaska or on the
Tongass National Forest. However, in some cases visitors may choose to
not come to southeast Alaska due to impacts from harvesting and road
construction; thus, these estimates are appropriate for inclusion in
the costs and benefits analysis.
Comments on ecosystem services. Commenters sought an effects
analysis disclosing how the rule will directly and indirectly impact
ecosystem services in the region, including economic cost and benefits
related to impacts on ecosystem services. There was concern that
exemption from the rule could lead to removal of trees and damage to
ecosystems which can adversely impact ecosystem services.
In response to the comments received, additional qualitative
information and discussion related to biological and physical ecosystem
services values has been added to the RIA between proposed and final
rule preparation. In addition, the cost-benefit analysis includes
quantitative estimates of forgone conservation value, from peer
reviewed research designed to facilitate the consideration of ecosystem
services in land management. Cost of forgone conservation value are
applied to the net-change in suitable old-growth acres across the
alternatives. While only a portion of suitable acres will be harvested,
the analysis includes an upper estimate of value associated with all
suitable old-growth acres and a lower estimate assuming all suitable
old-growth acres would be harvested over 100 years. This range of
estimates accounts for uncertainty application of value associated with
conservation demand.
Comments on road costs. Commenters sought cost data for road
building and maintenance (per mile) in the areas considered for
exemption from the rule.
The RIA for the final rule includes new information on road costs.
Road construction and decommissioning
[[Page 68700]]
costs are not considered since it is unlikely that they would be paid
by the agency given the influence of the limited export policy. In
2007, the Forest Service approved a limited export policy, and this
boost to appraised values has made rare the construction of roads by
the agency in advance of timber sales. Road maintenance costs are
considered quantitatively in the cost-benefit analysis of the final
rule and regulatory alternatives.
Comments on agency costs. Commenters were concerned that the
reduction in expenses from exempting the Tongass from the 2001 Roadless
Rule were not quantified. In addition, commenters disagreed with the
assertion that the rule would not increase agency costs because it
would not increase timber harvest levels and sought a more
comprehensive estimate of anticipated agency costs and losses from
below-cost timber sales. In addition, commenters asserted that analysis
should include an overall assessment of the Tongass timber program
costs including road costs. In addition, commenters noted the agency
costs section should also include the estimated cost for conducting
this rulemaking.
Details on agency costs from road maintenance have been added to
the RIA for the final rule in the RIA section called ``Agency Costs
including Control of Regulatory Costs''. Detailed analysis of
reductions in environmental compliance cost are not possible. This
final rule and the regulatory alternatives are programmatic, meaning
that they establish direction for broad land areas, rather than
schedule specific activities in specific locations. None of the
alternatives authorize any site-specific projects or other ground-
disturbing activities and, therefore, it is not possible to estimate
future activities and subsequent marginal changes in environmental
activities. However, potential incremental reductions in compliance
costs are noted in the RIA for the final rule. The cost of rulemaking
is the cost of managing NFS lands as a part of normal agency operation
and exists as part of the baseline 2001 roadless rule so there are not
incremental costs.
Comments on recreation and tourism. Some commenters suggested that
the recreation-related assessment provided in the RIA understated
potential impacts to the visitor industry because it considers only
changes in suitable timber acres and does not address indirect effects
to adjacent areas, whereas, timber harvest and road construction have
the potential to affect much larger areas than the area that is logged.
In addition, commenters expressed concern that the Forest Service did
not analyze the corresponding effects on rural communities from the
displacement of outfitters, guides, and tour operators.
The analysis of recreation in the RIA for the final rule is not a
site-specific review; rather, it uses available information to
illustrate broad patterns of use and differentiate between the
regulatory alternatives. It assumes all visitation, and half of
visitation, is displaced under the highest level of timber suitability
designation, under the final rule, to provide an upper- and lower
estimate of displacement, for a broad orders of magnitude comparison
with other costs and benefits. Assuming all visitation is displaced
considers not just effects on visitation occurring physically on lands
suitable for timber production but also effects on visitation in other
areas. The revised analysis also includes assessing the economic
importance of nature-based tourism in southeast Alaska, as measured by
business revenue, from data collected by the University of Alaska,
Anchorage.
Comments on the DEIS climate and carbon analysis. Commenters were
concerned that the DEIS analysis did not utilize the best available
science and the qualitative nature of the analysis is not sufficient.
The climate and carbon analysis in the DEIS and FEIS is based on
the best available science on carbon stocks and fluxes, and is
consistent with the latest literature including the Pacific Northwest
Research Station's Science Findings that became available after
publication of the DEIS (Forestry as a Natural Climate Solution: The
Positive Outcomes of Negative Carbon Emissions, March 2020). The DEIS
and FEIS analysis utilized Forest Inventory and Analysis data sets
specific to the Tongass National Forest to assess forest carbon stocks
and disturbance trends over a recent 20-year period. The influence of
potential future climate on the Forest was detailed using recent global
circulation model projections and relevant scientific literature
detailing climate impacts.
The foreseeable impacts of the final rule on carbon emissions and
forest carbon stocks are extremely small because the level of timber
harvesting is expected to be the same between implementation of the
2001 Roadless Rule and a full exemption. Therefore, a qualitative
approach is appropriate and sufficient.
Comments on the DEIS timber analysis--level of harvest. Commenters
were concerned that the timber analysis assumed no increased level of
timber harvest.
The level of harvest used in the DEIS and FEIS timber analysis is
based on the Forest Plan projected timber sale quantity of 46 MMBF feet
per year. This is a reasonable, conservative assumption for the
analysis because it is based on estimates of long-term market demands.
The Tongass National Forest actual volume sold was approximately 30.9
MMBF in fiscal year 2017, 9.3 MMBF in fiscal year 2018, and 5.6 MMBF in
fiscal year 2019. Thus, 46 MMBF remains a reasonable estimate to
utilize for effects analyses based on volume sold since 2016, when the
forest plan was most recently amended, and more importantly it remains
the agency's best estimate despite a few years of lower harvest levels.
The USDA recognizes the projected timber sale quantity is not a
cap, like the allowable sale quantity from the 1982 Planning Rule. It
is only an estimate, and at this time it is the agency's best estimate.
The agency has no reason to believe harvest levels will increase
from the 2016 Forest Plan annual projected timber sale quantity based
on implementation of the final rule. Although, the final rule will
increase the acres of old-growth available for harvest by about 168,000
acres, this opportunity is likely to be constrained by the
implementation of the young-growth transition strategy and the
economics of timber harvesting in general. As previously mentioned,
after 2032 the transition old-growth timber harvest will be limited to
5 MMBF per year, at which point entry into roadless areas will become
less attractive because there will be fewer high-volume acres to off-
set the cost of new road construction. As the young-growth matures and
becomes a greater proportion of the annual harvest, the Tongass timber
sale program will become more focused on previously roaded areas, where
the majority of the young-growth stands exist. In addition, between
2003 and 2011 when the Tongass National Forest was exempted from the
2001 Roadless Rule, only about 300 acres of timber were harvested
within IRAs. This indicates that there will likely not be a rush to
harvest old growth within roadless areas under the final rule.
Comments on the DEIS timber analysis--distribution of harvest.
Commenters were concerned that the DEIS timber analysis assumed old-
growth and young-growth harvest would be evenly disturbed across
suitable acres. Commenters were concerned this made it difficult to
fully
[[Page 68701]]
understand the impacts of the alternatives to a community.
Based on these concerns, the timber analysis was refined to
estimate where old growth is most likely to be harvested within the
suitable acreage over the next 100 years. Estimates considered timber
sale economics, old-growth volume, and timber sale history on the
Tongass National Forest. The result of the analysis is a shift of
expected timber harvest from the northern ranger districts to the
southern ranger districts. The biggest declines in the north are in the
Sitka and Hoonah ranger districts, and the largest increases are in the
Thorne Bay and Petersburg ranger districts.
Comments regarding environmental justice. Commenters expressed
concerns that tribal members rely on roadless areas for food security,
cultural practices, and their traditional way of life and that the
final rule would disproportionately impact them, which would be a
violation of environmental justice principles.
The final rule is programmatic and, as such, does not schedule
specific activities in specific locations. The final rule will increase
the acres available for timber harvest, but harvest levels are expected
to remain the same as they would under the 2001 Roadless Rule. The
amount of new or reconstructed road miles is expected to be similar as
the 2001 Roadless Rule. This makes it challenging to evaluate the
effects of the final rule on communities or populations. However, the
Civil Rights Impact Analysis (Departmental Regulation 4300-004)
recognizes that although the rule itself does not have a
disproportionate effect on any specific population, specific activities
associated with implementation of the Forest Plan within roadless areas
can have environmental justice implications. An opportunity for review
for environmental justice concerns will be available if and when
activities are proposed, and specific locations and extent are defined.
Regulatory Certifications
Regulatory Planning and Review
The OMB determined this rulemaking to be a significant regulatory
action as it may raise novel legal or policy issues arising out of
legal mandates, the President's priorities, or the principles set forth
in Executive Order 12866. The agency has prepared a regulatory
requirements analysis of impacts and discussion of benefits and costs
of the final rule.
The final rule exempting the Tongass National Forest from the 2001
Roadless Rule will provide additional opportunities for timber harvest
and road construction to occur; however, it does not materially affect
the total quantity of timber expected to be harvested or miles of new
roads constructed. As to timber harvest activities, the final rule
would increase the flexibility for land managers to locate and design
timber sales. Improved flexibility could, in turn, improve the Forest
Service's ability to offer economic sales that meet timber industry
needs and contribute to rural economies. While many factors can
influence the cost of timber harvest, areas along existing roads or
those using marine access facilities are typically more economically
efficient, followed by areas where existing roads can be easily
extended. The most expensive harvesting costs are associated with areas
without existing road or marine access facilities.
Cost savings from improved flexibility for timber harvest
activities would accrue alongside other benefits, including reduced
costs for leasable mineral availability and increased potential for
development of renewable energy and transportation projects. While many
of these activities were allowed under the 2001 Roadless Rule, industry
advocates believe that the 2001 Roadless Rule discouraged private
sector investment in projects within roadless areas. Although it is
difficult to estimate the extent of investments that did not occur due
to fear of regulatory burden, the perception of this does affect the
level of investment, and the final rule will eliminate that concern.
Stumpage value benefits are quantified alongside agency road
maintenance costs, cost of forgone conservation value, estimated lost
revenue to outfitters and guides from visitors potentially displaced by
annual harvest of suitable young- and old-growth, and forgone value of
access to recreationists not using outfitter and guides. Dollars spent
by visitors are not necessarily lost but subject to displacement-
related changes. Some businesses may lose revenue if visitors choose
not to travel to southeast Alaska, but others may see increases in
revenue if visitors choose to stay longer or travel to substitute sites
within southeast Alaska. Discounted upper bound estimates of net
present value are positive for the final rule and regulatory
alternatives.
Regulatory Flexibility Act and Consideration of Small Entities
The USDA certifies that the final rule does not have a significant
economic impact on a substantial number of small entities as determined
in the Regulatory Flexibility Analysis because the final rule does not
directly subject small entities to regulatory requirements. Therefore,
notification to the Small Business Administration's Chief Council for
Advocacy is not required pursuant to Executive Order 13272. A number of
small and large entities may experience time or money savings as a
result of flexibility provided by the final rule, or otherwise benefit
from activities on NFS lands under the final rule.
Paperwork Reduction Act
This final rule does not require any additional record keeping,
reporting requirements, or other information collection requirements as
defined in 5 CFR part 1320 that are not already approved for use and,
therefore, imposes no additional paperwork on the public. Accordingly,
the review provisions of the Paperwork Reduction Act of 1995 (44 U.S.C.
3501 et seq.) and its implementing regulations at 5 CFR part 1320 do
not apply.
Regulatory Risk Assessment
A risk assessment is only required under 7 U.S.C. 2204e for a
``major'' rule, the primary purpose of which is to regulate issues of
human health, human safety, or the environment. The statute (Pub. L.
103-354, Title III, Section 304) defines ``major'' as any regulation
the Secretary of Agriculture estimates is likely to have an impact on
the U.S. economy of $100 million or more as measured in 1994 dollars.
Economic effects of the final rule are estimated to be less than $100
million per year.
Reducing Regulation and Controlling Regulatory Costs
Executive Order 13771, Reducing Regulation and Controlling
Regulatory Costs, issued January 30, 2017, requires that significant
new regulations shall, to the extent permitted by law, be offset by the
elimination of existing costs associated with at least two prior
regulations.
The final rule has been reviewed in accordance with Executive Order
13771 on reducing regulation and controlling regulatory costs and is
considered an Executive Order 13771 deregulatory action.
Federalism
The USDA has considered the final rule in context of Executive
Order 13132, Federalism, issued August 4, 1999. The USDA has determined
the final rule conforms with federalism principles set out in Executive
Order 13132, would not impose any compliance costs on any state, and
[[Page 68702]]
would not have substantial direct effects on states, on the
relationship between the National Government and the State of Alaska,
or any other state, nor on the distribution of power and
responsibilities among the various levels of government. Therefore, the
USDA concludes that this final rule does not have federalism
implications. The final rule is based on a petition submitted by the
State of Alaska under the APA (5 U.S.C. 553(e)) and pursuant to USDA
regulations at 7 CFR 1.28. The final rule responds to the State of
Alaska's petition, considers public comment received during the Forest
Service's public comment periods, and considers input received from
cooperating agencies. The State of Alaska is a cooperating agency
pursuant to 40 CFR 1501.6 of the Council on Environmental Quality
regulations for implementing the procedural provisions of the NEPA.
No Takings Implications
The USDA has considered the final rule in context with the
principles and criteria contained in Executive Order 12630,
Governmental Actions and Interference with Constitutionally Protected
Property Rights, issued March 15, 1988. The USDA has determined that
the final rule does not pose the risk of a taking of private property
because it only applies to management of NFS lands and contains
exemptions that prevent the taking of constitutionally protected
private property.
Consultation With Indian Tribal Governments
On July 30, 2018, the Forest Service initiated government-to-
government consultation with 32 Alaska federally recognized tribes and
27 Alaska Native corporations, and invited them to participate as
cooperating agencies during the rulemaking process. Six tribes
initially agreed to become a cooperating agency including Angoon
Community Association, Central Council Tlingit and Haida Indian Tribes
of Alaska, Hoonah Indian Association, Hydaburg Cooperative Association,
Organized Village of Kake, and Organized Village of Kasaan. The
Organized Village of Kake withdrew as a cooperating agency after
publication of the proposed rule, and the remaining tribal cooperating
agencies withdrew after the publication of the FEIS in collective
protest over the identification of the full exemption alternative as
the preferred alternative in the FEIS. Periodic cooperating agency
meetings were held throughout the rulemaking process that included the
tribal cooperating agencies. Furthermore, government-to-government
consultations occurred by request and twelve consultation meetings were
held throughout the rulemaking process. Two of the twelve government-
to-government consultation meetings were conducted by USDA Under
Secretary James Hubbard and the remaining ten meetings were conducted
by the Alaska Region of the Forest Service.
On July 21, 2020, the Secretary of Agriculture received a petition
from nine southeast Alaska Tribal governments, requesting the United
States government to commence a new rulemaking in collaboration with
Tribes to create a Traditional Homelands Conservation Rule to identify
and protect traditional and customary uses of the Tlingit, Haida, and
Tsimshian peoples in the Tongass National Forest. This petition also
requests the USDA create a new process for engaging in consultation
with Tribes based on the principle of ``mutual concurrence''. The
petition states that it was submitted in response to the Tribes'
experience in the Alaska Roadless Rulemaking process and their belief
that their contributions were not adequately considered. The petition
is currently under review by the Secretary.
The final rule was reviewed in accordance with the requirements of
Executive Order 13175, Consultation and Coordination with Indian Tribal
Governments. Executive Order 13175 requires federal agencies to consult
and coordinate with tribes on a government-to-government basis on
policies that have tribal implications, including regulations,
legislative comments, or proposed legislation, and other policy
statements or actions that may have substantial direct effects on one
or more Indian tribes, on the relationship between the Federal
Government and Indian tribes, or on the distribution of power and
responsibilities between the Federal Government and Indian tribes.
The USDA's Office of Tribal Relations assessed the impact of the
final rule on Indian tribes and determined the final rule has tribal
implications that require continued outreach efforts in the
implementation of the final rule to determine if tribal consultation
under Executive Order 13175 is required. To date, as part of the
regulatory review process noted above, the Forest Service conducted
various outreach efforts to American Indian and Alaska Native tribes,
villages, and corporations regarding the development of this final
rule, and the tribal cooperation in this process.
If a tribe requests consultation, the Forest Service will work with
the USDA Office of Tribal Relations to ensure meaningful consultation
is provided where changes, additions, and modifications identified
herein are not expressly mandated by Congress.
Civil Justice Reform
The USDA reviewed the final rule in context of Executive Order
12988. The USDA has not identified any state or local laws or
regulations that conflict with the final rule or would impede full
implementation of the rules. However, if the rule is adopted, all state
and local laws and regulations that conflict with this rule or would
impede full implementation of this rule would be preempted. No
retroactive effect would be given to this rule, and the final rule
would not require the use of administrative proceedings before parties
could file suit in court.
Unfunded Mandates
Pursuant to Title II of the Unfunded Mandates Reform Act of 1995 (2
U.S.C. 1531-1538), signed into law on March 22, 1995, the USDA has
assessed the effects of the final rule on state, local, and tribal
governments and the private sector. The final rule does not compel the
expenditure of $100 million or more by any state, local, or tribal
government, or anyone in the private sector. Therefore, a statement
under section 202 of the Act is not required.
Energy Effects
The USDA has considered the final rule in context of Executive
Order 13211, Actions Concerning Regulations That Significantly Affect
Energy Supply, Distribution, or Use, issued May 18, 2001. The USDA has
determined the final rule does not constitute a significant energy
action as defined in Executive Order 13211. Therefore, a statement of
energy effects is not required.
E-Government Act
The USDA is committed to complying with the E-Government Act, to
promote the use of the internet and other information technologies to
provide increased opportunities for citizen access to government
information and services, and for other purposes.
List of Subjects in 36 CFR Part 294
National forests, Navigation (air), Recreation areas, Roadless area
management.
0
For the reasons set forth in the preamble, the USDA amends part 294 of
title 36 of the Code of Federal Regulations by adding subpart E,
consisting of Sec. Sec. 294.50 and 294.51, to read as follows:
[[Page 68703]]
PART 294--SPECIAL AREAS
Subpart E--Alaska Roadless Areas Management
Authority: 16 U.S.C. 472, 529, 551, 1608, 1613; 23 U.S.C. 201,
205.
Sec. 294.50 Tongass National Forest.
Subpart B of this part, revised as of July 1, 2001, shall not apply
to the Tongass National Forest.
Sec. 294.51 Transition.
The Tongass Forest Supervisor shall issue a ministerial Notice of
Administrative Change pursuant to 36 CFR 219.13(c) identifying plan
changes made in conformance with the regulatory determinations of this
subpart; specifically, the portion of the December 9, 2016, Record of
Decision concerning suitable timber lands attributed exclusively to
implementation of the January 12, 2001, Roadless Area Conservation Rule
(see 36 CFR part 294, revised as of July 1, 2001) shall be designated
as suitable.
Dated: October 26, 2020.
Stephen Censky,
Deputy Secretary of Agriculture.
[FR Doc. 2020-23984 Filed 10-28-20; 8:45 am]
BILLING CODE 3411-15-P