Notice of Final Action To Adopt Revisions to the Bureau of Land Management's Procedures for Managing the NEPA Process, Chapter 11 of the Department of the Interior's Manual Part 516, 45504-45542 [E7-15746]
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Federal Register / Vol. 72, No. 156 / Tuesday, August 14, 2007 / Notices
DEPARTMENT OF THE INTERIOR
Bureau of Land Management
[516 DM 11; WO–210–1610 24 1A]
Notice of Final Action To Adopt
Revisions to the Bureau of Land
Management’s Procedures for
Managing the NEPA Process, Chapter
11 of the Department of the Interior’s
Manual Part 516
Bureau of Land Management,
Interior.
ACTION: Notice of final action.
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AGENCY:
SUMMARY: The Bureau of Land
Management (BLM) gives notice of
revised policies and procedures for
implementing the National
Environmental Policy Act (NEPA), as
amended, Executive Order (E.O.) 11514,
as amended, E.O. 12114, and Council on
Environmental Quality (CEQ)
regulations implementing NEPA. These
final implementing procedures are being
issued as Chapter 11 of the Department
of the Interior’s Departmental Manual
Part 516 (516 DM 11) and supersedes
previous implementation guidance.
These revisions update the procedures
used to implement NEPA for actions
taken in managing public lands. The
BLM’s NEPA compliance procedures
can be found at the Department of the
Interior (DOI) Electronic Library of
Interior Policies (ELIPS) https://
elips.doi.gov.
The following sections in 516 DM 11
(dated 5/27/04) are affected by this
Federal Register notice: Purpose (11.1);
NEPA Responsibilities (11.2); External
Applicant’s Guidance (11.3); General
Requirements (11.4), Parts A–G; Plan
Conformance (11.5); Existing
Documentation (11.6), Parts A–E;
Actions Requiring an Environmental
Assessment (11.7), Parts A–E; and
Actions Eligible for Categorical
Exclusions (11.9), categories B–D and
G–J. New sub-parts have been added to
the Oil, Gas and Geothermal Energy (B),
Forestry (C), and Rangeland
Management (D) categories. Two new
categories have been added: Recreation
Management (H) and Emergency
Stabilization (I). Transportation category
sub-parts G(1), (2), and (3) have been
expanded to include trails.
DATES: Effective Date: The revised 516
DM 11, including changes and additions
to the categorical exclusions (CXs), is
effective upon the date of publication of
this notice in the Federal Register.
ADDRESSES: The BLM’s revisions to 516
DM 11 can be accessed electronically
via the Internet at https://elips.doi.gov.
Hard copies are available by contacting
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Peg Sorensen, Division of Planning and
Science Policy, at 202–452–0364.
FOR FURTHER INFORMATION CONTACT: Peg
Sorensen, Division of Planning and
Science Policy, at 202–452–0364.
SUPPLEMENTARY INFORMATION: Final
revised NEPA procedures for the DOI
were published in the Federal Register
(69 FR 10866–10866, March 8, 2004),
and (70 FR 32840–32844, June 6, 2005).
The DOI bureau and office specific
procedures are published as chapters in
Part 516 of the Departmental Manual.
The 516 DM 11 addresses the BLM
policy and procedures to assure
compliance with the spirit and intent of
NEPA.
A notice of the proposed revisions to
the BLM’s ‘‘National Environmental
Policy Act Revised Implementing
Procedures’’ for 516 DM 11 was
published in the Federal Register (71
FR 4159–4167, January 25, 2006), with
additional information available at
https://www.blm.gov/planning/
news.html. A 30-day public comment
period followed that publication.
Consideration of the comments received
resulted in the following modifications
to the proposed revised implementing
procedures.
11.1. Purpose: No Change.
11.2. NEPA Responsibilities: Edited
title to emphasize that there are
multiple responsibilities.
Parts A–E: Edited to improve
readability.
Parts B–E: Clarified executive and
delegated leadership responsibilities.
Parts E & F: Moved sub-part E(1) to a
new part F.
11.3. External Applicants’ Guidance:
Edited title to clarify that this section
only applies to external applicants who
are proposing an action. Language was
added from the NEPA to clarify text
within the section.
Part A. General, sub-parts A(2)–(4):
Edited to improve readability.
Sub-part A(3): Replaced the ‘‘State
Director’’ with ‘‘the Responsible
Official’’ to clarify that the authorized
activity is not limited to State Directors.
Part B. Regulations, preamble: Edited
to improve readability.
11.4. General Requirements:
Part A–H: Revised section titles to
create parallel structure. Edited and
reorganized all sections to clarify
requirements and improve readability.
Part A: Added ‘‘integrating NEPA
requirements with other environmental
review and consultation requirements’’
(from the former part D) to reduce
paperwork and delays.
Part B: Addressed the elimination of
duplicate tribal, State, and local
government procedures, and the use of
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common databases and joint planning
processes, meetings, investigations, and
NEPA analyses.
Part C: Addressed consultation and
coordination requirements.
Part D, sub-parts (1) & (2): Addressed
public involvement requirements.
Eliminated the reference to ‘‘consensusbased decision-making’’ and replaced it
with ‘‘consensus-based management’’ to
be consistent with direction provided by
the DOI. Inserted the DOI’s definition of
‘‘consensus-based management’’ and
expectations regarding the process.
Part E: Redefined ‘‘adaptive
management’’ to match the DOI
definition.
Part F: Clarified a training
requirement for the BLM employees
facilitating public and community
involvement.
Part G: Clarified action limits during
environmental review.
11.5 Plan Conformance: Edited to
improve readability. Clarified what the
Responsible Official’s options are when
a proposed action does not conform to
an approved plan.
11.6 Existing Documentation
(Determination of NEPA Adequacy):
Edited the title to create a section
header that conforms to a standardized
format. This section was rewritten to
clarify the BLM’s policy regarding the
use of existing documentation.
Operational information on how to
conduct a Determination of NEPA
Adequacy (DNA) will be provided in the
BLM NEPA Handbook (H–1790–1).
11.7 Actions Requiring an
Environmental Assessment (EA):
Part A: Moved part A information to
a new part D. Part A now defines the
purpose and need for an EA.
Part B: Inserted a new requirement to
consult 40 CFR 1508.9(b) which
outlines ‘‘discussion’’ requirements in
an EA.
Part C: Edited to clarify and enhance
general understanding of when an EA is
appropriate.
Part D: Directs the Responsible
Official to consider an EA if there are
uncertain impacts.
Part E: This new part directs the
Responsible Official to prepare an
Environmental Impact Statement (EIS) if
it is determined that a CX or an EA is
not appropriate. Removed unnecessary
text ‘‘processed in accordance with 40
CFR 1502.’’
11.8 Major Actions Requiring an
Environmental Impact Statement (EIS):
Part A(1): Refined the text to clarify
criteria used to consider when
determining whether to prepare an EIS
level analysis or not. Removed the
following statement: ‘‘or the impact
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analysis of an action is likely to be
highly controversial.’’ This edit was
made to clarify the criteria the BLM
considers when determining whether an
EIS level analysis is needed.
Supplementary guidance on how to
determine significance when
considering whether to prepare an EIS,
such as when effects should be
considered ‘‘highly controversial,’’ will
be placed in the BLM NEPA Handbook
(BLM H–1790–1).
Part B: Dropped the term
‘‘Wilderness’’ from the list of actions
typically requiring an EIS. This edit
reflects current program policy that
there will no longer be proposals to
designate Wilderness Areas under
Section 603 of FLPMA. Supplementary
guidance on how to implement policy
regarding preparation of EISs will be
placed in the BLM NEPA Handbook
(BLM H–1790–1).
Part C: Removed unnecessary text
‘‘processed in accordance with 40 CFR
1501.4(e)(2).’’
11.9 Actions Eligible for a
Categorical Exclusion:
Preamble: Replaced ‘‘exceptions’’
with ‘‘extraordinary circumstances’’ to
reflect a revision to 516 DM 2.3A(3)
made by the DOI in June 2005. Added
a statement identifying the DOI-wide CX
in 516 DM 2, appendix 1, available for
the BLM consideration. The BLM
reviewed supporting data and
conclusions of no significant effect for
all proposed CXs based on comments
received. Identified below are revisions
to final CX language based on this
review. Some additional information
was added to the administrative file
based on the review. In addition, the
BLM reviewed the proposed CXs and
this final action establishing the final
CXs in light of CEQ’s proposed
guidance, ‘‘Establishing, Revising and
Using Categorical Exclusions under the
National Environmental Policy Act,’’ (71
FR 54816–54820, September 19, 2006).
The BLM believes that the
establishment of the new CXs is
consistent with CEQ’s proposed
guidance. Based on discussions, review,
and to clarify the intent of the BLM,
language has been added indicating the
need for all proposed actions and
activities to be, at a minimum,
consistent with the DOI and the BLM
regulations, manuals, handbooks,
policies, and applicable Land Use Plans
(LUP) regarding design features, Best
Management Practices, Terms and
Conditions, Conditions of Approval,
and Stipulations.
A. Fish and Wildlife: Fixed a
typographical error in sub-category (2)
by replacing ‘‘value’’ with ‘‘valve.’’
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B. Oil, Gas, and Geothermal Energy:
Sub-category (6): Removed text
‘‘including the establishment of terms
and conditions,’’ and edited language to
more accurately describe the actions
covered.
Sub-category (7): The BLM has
decided not to finalize this proposed CX
(CX B(7)) for the category of actions
described as, ‘‘approving the drilling or
subsequent operations of a geothermal
well within a developed field for which
a LUP and/or an environmental
document, prepared pursuant to NEPA,
analyzed such drilling as within the
scope of a reasonably foreseeable future
activity.’’ When these actions are within
the scope of the previous NEPA
document and sufficiently analyzed
therein, and that determination is
documented, no further NEPA analysis
is required. In consultation with CEQ,
the BLM has decided that more focused
NEPA documents should be prepared at
the outset to support subsequent
implementation of the geothermal field
development plan or utilization plan,
and that this practice, combined with a
DNA, would provide a more appropriate
method for streamlining the
documentation of the evaluation of
subsequent infill well proposals than a
new CX.
Sub-category (8): The BLM has
decided not to finalize this proposed
CX. In consultation with CEQ, it was
determined that the action of issuing a
geothermal site license or operational
permit (CX B(8)) is an administrative/
ministerial function subsequent to the
approval of a utilization plan. Approval
of a utilization plan involves analysis of
the environmental effects of
constructing and operating the planned
facility. The administrative action of
issuing the site license and permit to
operate does not result in additional
environmental effects. Therefore, the
BLM will eliminate this additional
NEPA review, as unnecessary and
redundant.
C. Forestry:
Sub-category (6): Modified the
proposed language and format to
eliminate confusion about the sample
tree area limitation and restricted
activities. Added Lakeview District,
Klamath Falls Resource Area to the list
of locations where this CX may be used.
The Resource Area was mistakenly left
out of the proposed limitation and is
now included because the effects are
comparable to the others previously
listed in this section.
Sub-categories (7)–(9): Modified the
proposed format and syntax. Text that
defines and limits ‘‘temporary road’’
building activities was added to be
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consistent with the U.S. Forest Service
(FS) standards and regulations. Text that
defines and clarifies ‘‘a dying tree’’ was
added for purposes of this category of
actions.
Sub-category (9): Modified the
example (a) by replacing southern pine
beetle with mountain pine beetle to
represent a type of beetle that occurs in
western Oregon.
D. Rangeland Management:
The National Research Council
published Rangeland Health: New
Methods to Classify, Inventory, and
Monitor Rangelands in 1994. The
concepts identified in that publication
were incorporated in the BLM’s grazing
regulations and the agency used the
term ‘‘rangeland health’’ in much of
their initial policy and guidance related
to implementing those grazing
regulations. Although the term
‘‘rangeland health’’ was first introduced
in the grazing regulations, the
‘‘rangeland health standards’’ really
apply to the condition of the land itself
regardless of the uses that may influence
the health of that land. As a result, the
BLM has begun using the term ‘‘land
health’’ to avoid the misperception that
these concepts only apply to the grazing
program. For this reason, the term ‘‘land
health’’ is used in the description of this
proposed CX, even though both terms
are likely to be found within this
document or in other background
material supporting this document. Use
of the term ‘‘land health’’ does not
represent any substantive change in the
original definition, concept or use of the
term ‘‘rangeland health’’ and the reader
should view these terms as
interchangeable. The proposed
rangeland management sub-categories
(10) and (11) are finalized with the
following changes:
Sub-category (10): Lettered the bullet
statements, so the first bullet is criteria
(a); moved text (bullets two & three)
‘‘shall be conducted consistent with the
BLM and Departmental procedures and
applicable land and resource
management plans (RMP);’’ from here to
the general CX introduction to reflect
that text applies more generally and not
only to this CX. Modified text of bullet
four to exclude use of this CX for
otherwise qualifying ‘‘vegetation
management activities’’ in Wilderness
Study Areas and text becomes new
criteria (b). Modified bullet five to
become criteria (c) and added text to
indicate that the CX cannot be used for
biological treatments. Finally, added
text to define and limit the use of
temporary roads as criteria (d) and (e).
Sub-category (11): Moved criteria (a)
to (b) and modified the phrase ‘‘not
meeting standards solely due to factors
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other than existing livestock grazing’’ to
‘‘not meeting land health standards due
to factors that do not include existing
livestock grazing.’’ Changed the text to
clarify that the CX requires land health
assessments be completed prior to
considering the application of the CX.
Dropped proposed criteria (b) and
replaced it with criteria (a) that limits
the leases/permits eligible for the CX to
those where the lease/permit is
consistent with the use specified in the
previous lease/permit, there is no
change in the type of livestock, the
previously authorized active use is not
exceeded, and grazing does not occur
more than 14 days earlier or later than
specified on the previous lease/permit.
Sub-category (12): Dropped the
proposed CX based on further review of
supporting data.
E. Realty:
The proposed revision of sub-category
(16) was dropped upon further review.
F. Solid Minerals: No change was
proposed or made.
G. Transportation:
Sub-categories (1), (2), and (3): The
word ‘‘existing’’ which originally was
used in (1) and (2) has been eliminated
because it was potentially confusing,
and the words ‘‘and trails’’ have been
approved as proposed.
Sub-category (1) and (2): Replaced
‘‘Incorporating’’ for ‘‘Placing’’ in subcategory (1), and added ‘‘eligible’’ to
modify the language to clarify that only
roads and trails meeting criteria
developed in a LUP are to be
incorporated into the transportation
plan, or be subject to the actions
specified in sub-category (2).
H. Recreation Management:
Sub-category (1): The proposed
revision of the previous Category ‘‘H.
Other’’ to ‘‘Recreation Management and
sub-category ‘‘H(5)’’ to ‘‘H(1)’’ was
approved as revised. Increased the day
and overnight use threshold to 14
consecutive nights to be consistent with
the practice of Responsible Officials
under provisions in Title 43 of the Code
of Federal Regulations (CFR) that allow
such officials to set allowable length of
stay applicable to any casual visitor
using public lands (See 43 CFR 8365.1–
2 ‘‘Occupancy and Use,’’ and 43 CFR
8365.1–6 ‘‘Supplementary Rules’’). This
change has also been made to provide
consistency with the typical length of
stay for any casual visitor using public
lands (43 CFR 8364). Changed wording
from ‘‘contiguous acres’’ to ‘‘staging area
acres’’ to better define the limits on area
of impact. Replaced ‘‘travel management
areas or networks that are designated in
an approved LUP’’ with ‘‘recreational
travel along roads, trails, or in areas
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authorized in a LUP’’ because of
confusion over what constitutes a travel
management area or network. Text was
added to include a limitation that this
CX cannot be used for the establishment
or issuance of Special Recreation
Permits (SRP) for ‘‘Special Area’’
management (43 CFR 2932.5). The
requirement for Special Area SRPs and
the issuance of individual SRPs in
‘‘Special Areas’’ must be directed by
specific land use planning decisions
and commensurate NEPA analysis.
I. Emergency Stabilization: This new
section was adopted as proposed with
the addition of text to define and limit
the use of temporary roads. The section
included a requirement to treat
temporary roads for rehabilitation.
Sub-category (1)(e): Moved text ‘‘shall
be conducted consistent with the BLM
and the Department procedures,
applicable land and RMPs.’’ to general
CX introduction to reflect that text
applies more generally and not only to
this CX. Renumbered numbered criteria
based on the removal of this text.
J. Other: The previous existing subpart H was moved to sub-part J and
adopted as proposed with one
exception. An existing CX was
mistakenly left out of the January 25,
2006, Federal Register notice. The
following existing CX will be placed in
sub-part J (12): ‘‘Rendering formal
classification of lands as to their mineral
character and waterpower and water
storage values.’’ There is no change to
the language.
Appendix 11.1: The DNA Worksheet
appendix was deleted. Supplemental
guidance regarding the use of Existing
Documentation remains in section 11.6.
Comments on the Proposal
The BLM received more than 72,000
‘‘comments’’ during the 30-day
comment period (January 25, 2006, to
February 24, 2006). A ‘‘comment’’ is a
single, whole submission that may take
the form of a letter, postcard, email, or
fax. These comments came from private
citizens, elected officials, and groups
and individuals representing
businesses, private organizations, and
state and federal agencies. All
comments received were considered in
preparing this final action notice.
Public comment on the proposed
revisions addressed a wide range of
topics. Many comments support one or
more of the proposed revisions or favor
broadening the scope of the revision,
while many others oppose one or more
of the proposed revisions or recommend
more narrowly limiting the qualifying
criteria for a particular CX. Some
comments state that the 30-day
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comment period provided insufficient
time to review and comment on the
BLM’s proposed revisions. The BLM
received extensive and varied comments
during the 30-day comment period.
Based on this robust response, the BLM
determined that it was unnecessary to
extend the public comment period.
Some general comments state that the
BLM is using dated and inadequate
scientific information to support
management decisions. They
recommend that the BLM adopt a
specific process to systematically
incorporate the best available science in
all elements of the BLM public lands
management. The BLM Science Strategy
(September 2000) discusses the role of
science in the BLM management of the
public lands, and articulates a
conceptual framework for integrating
science into the BLM decision-making
process. Relevant scientific information
is brought to the decision-maker’s
attention by members of the
interdisciplinary team of professionals,
and through contract and in-house
investigations, science sharing forums,
and technical reports. In addition, the
public, cooperators and partners bring
scientific information forward during
the environmental review process.
Many comments addressed matters
beyond the scope of the proposed
revisions to the 516 DM 11. These
included requests for the BLM to add
policy statements to the 516 DM 11
pertaining to conformance with the
Clean Air Act, preserving and honoring
valid existing rights, and conducting
cost-benefit analyses. Some comments
addressed land management activities
that were neither proposed nor
analyzed. Some comments state that
grazing is incompatible with good land
stewardship. Other comments suggested
that the proposed changes to 516 DM 11
‘‘denied [the public] their constitutional
rights’’ or would ‘‘cause unrestricted
use’’ of public lands. Responses to most
out-of-scope comments are not
provided.
Responses to Specific Comments on
Sections 11.1–11.8
11.1 Purpose
Comment: Some comments ask how
to access 516 DM 11 and the DOI’s
Environmental Statement Memoranda
(ESM).
Response: The BLM provided the Web
site address to access procedures (516
DM 11) that are being replaced by this
Federal Register notice in the Summary
portion of 71 FR 4159–4167, January 25,
2006. The proposed changes to these
procedures were published in full in the
same Federal Register notice and were
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posted on the DOI, ELIPS Web site in
the Departmental Manual chapters at
https://elips.doi.gov. The DOI’s ESMs can
be accessed through the DOI’s Web site
at https://www.doi.gov/oepc via the
descriptions in the left-hand column.
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11.3 External Applicants’ Guidance
Comment: Some comments ask for
information to guide applicants
interested in the BLM program
regulations.
Response: The purpose of this section
is to provide guidance to external
parties making applications to the BLM.
The title has been changed to make this
clear. A list of potentially relevant
regulations is located in part B.
Additional regulations, policies,
directives, and guidelines that affect
BLM programs may be provided when
the applicant contacts a Responsible
Official and describes their proposed
action(s).
Comment: A concern was expressed
about the absence of NEPA compliance
in the ‘‘applicants’’ guidance’’ section.
Response: The text has been clarified
to address NEPA requirements for
private applicants and other non-federal
entities as required by 40 CFR 1501.2(d).
11.4 General Requirements
Comment: Some comments state that
local, state, and federal agencies should
not be provided ‘‘cooperating agency
status’’ because it blurs the lines of
NEPA responsibility.
Response: The NEPA regulations
specifically provide for and encourage
the use of ‘‘cooperating agencies’’ (40
CFR 1501.6). The participation of other
agencies in the BLM’s NEPA processes
in no way ‘‘blurs’’ the BLM’s status as
the agency responsible for the NEPA
analysis and the associated decisionmaking affecting public lands.
Comment: Some comments ask the
BLM to revise the language regarding
consensus-based decision-making to
clarify that only federal managers have
decision-making authority.
Response: The new language in 516
DM 11.4 D(2) has been added to
describe consensus-based management
(as per ESM 03–7) and to clarify that the
BLM has exclusive responsibility for
decision-making.
Comment: Some comments
recommend that more detailed guidance
be placed in 516 DM 11 to promote
consistency between the BLM offices
undertaking public involvement.
Response: The recommended detailed
guidance will be considered for
placement in the BLM’s NEPA
Handbook (H–1790–1). The BLM’s
public involvement guidance in 516 DM
11 is consistent with policies and
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procedures specified in the NEPA, E.O.s
11514 and 12114, and CEQ regulations.
Federal decision-makers have discretion
as to how they enable public
involvement because of the broad range
and variety of potential proposed
actions and public interests at stake.
Comment: Some comments state that
the BLM should revise 516 DM 11 to
require public notice about ‘‘decision
documents’’ and Findings of No
Significant Impacts (FONSIs)
statements.
Response: The CEQ regulations
implementing the NEPA have specific
public notification requirements. The
BLM will consider adding more specific
guidance regarding public notice of a
FONSI in the BLM NEPA Handbook (H–
1790–1). Distinct from its obligations
under the NEPA, the BLM is required
under other statutes to provide public
notification regarding management
decisions. This notification is done in
accordance with program specific
regulations and guidance.
Comment: Some comments state that
the public’s involvement in the NEPA
process should be more limited, while
other comments state that the public
should be given more involvement
opportunities than they are currently
provided.
Response: The CEQ regulations
implementing the NEPA require
agencies to involve the public in the
environmental analysis process. The
timing of public involvement for EISs is
set by regulation; however, the timing
and manner of the subject involvement
for EAs and CXs is left to the discretion
of the Responsible Official. The BLM is
not changing existing public
involvement procedures as a part of the
process of revising this 516 DM 11.
Comment: Some comments suggested
that the BLM revise 516 DM 11 to
provide further guidance regarding
facilitating public involvement during
NEPA review processes.
Response: Because the range of
activities the BLM undertakes is so
broad and varied, and because public
involvement can take many forms,
specific guidance on facilitating such
public involvement is more appropriate
for inclusion in the BLM’s NEPA
Handbook (H–1790–1). The NEPA
Handbook provides operational
guidance on how to implement the BLM
policy regarding public involvement.
Comment: Some comments state that
the BLM should revise the language in
section 11.4 to include reference to the
Data Quality Act (Pub. L. 106–554).
Response: Specific reference to the
Data Quality Act in 516 DM 11 was not
added. The BLM managers are
responsible for ensuring compliance
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with all applicable laws and regulations
including the Data Quality Act.
Comment: Some comments ask the
BLM to prevent excessive data
collection during the NEPA analysis.
Response: The BLM uses best
available data or collects new data
appropriate to the level of the NEPA
analysis needed to make an informed
decision regarding the proposed action.
The provisions described in 516 DM
11.4(A–C) are intended to aid in this
effort, provided that the data and
analysis compiled by other permitting
agencies is complete, available and
sufficient to meet the BLM’s needs.
Comment: Some comments express
concern that direction for limiting
actions during the NEPA analysis
process was too narrowly framed and
did not adequately reflect regulatory
requirements.
Response: In addition to noting these
limits, the BLM revised section 11.4G to
refer readers directly to the CEQ
regulation regarding the limitation on
action during the NEPA analysis as
provided in 40 CFR 1506.1, and to
provide guidance to aid in fulfilling the
regulations.
Comment: Some comments point out
that the Federal Register notice failed to
use the DOI’s most recently adopted
definition of adaptive management
(AM).
Response: The BLM revised the AM
definition in 516 DM 11.4E to be
consistent with the DOI definition
found in 516 DM 4.16.
Comment: Some comments question
the use of AM and request more
information about when it should be
used. There is concern that AM not be
used as sole mitigation to justify a
FONSI.
Response: The BLM does not use AM
as a sole mitigation to justify a FONSI.
Section 11.4E states that the
Responsible Official is encouraged to
build AM practices into proposed
actions and NEPA compliance activities
and train personnel in this important
environmental concept. The DOI is
developing additional guidance for
bureaus on the use of an AM approach
to management activities.
Comment: Some comments state that
using AM violates the NEPA by (1)
allowing the BLM to defer decisions
regarding mitigation—and the impacts
that might result if the mitigation fails—
without addressing those decisions in a
NEPA document; (2) removing
significant agency decisions about
mitigation, and the possible impacts,
from public review and comment; (3)
removing significant impacts that may
be detected during the monitoring
process from NEPA analysis; and (4)
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relying heavily on monitoring and
evaluation, which the BLM is often
unable to support.
Response: (1) Adaptive Management
is a planning tool; it does not relieve the
BLM of the responsibility of meeting the
requirements of the NEPA or other laws.
The use of AM does not permit the BLM
to defer ‘‘decisions on mitigation and
impacts if mitigation fails.’’ In fact, a
more vigorous monitoring strategy will
help determine if mitigation is working,
and if not, it will help speed up the
change in management action or
mitigation strategy. Mitigation and
impacts will still be addressed in the
NEPA document as will the AM process
itself. Adaptive Management will not be
applied to all resource decisions made.
(2) Stakeholder involvement is a critical
aspect of AM. New DOI policy clearly
links stakeholder involvement to
implementation of AM from plan
development through implementation.
Agency decisions on mitigation and
impacts will not be removed from
public review and comment and it is
hoped that there will be an increased
level of public involvement. (3)
‘‘Significant impacts’’ that are detected
during monitoring will not be removed
from the NEPA analysis. Rather, any
actions taken to address ‘‘significant
impacts’’ that may arise will themselves
be subject to appropriate NEPA review,
including appropriate public
involvement. It is hoped that a more
vigorous stakeholder involvement
process using AM will improve the
BLM’s ability to detect impacts earlier
and make the necessary resource
management changes in partnership
with stakeholders. (4) The AM process
will only be used when adequate
monitoring and evaluation can be
assured. Successful AM is dependent on
good monitoring and evaluation. If the
monitoring strategy goes unfulfilled, the
BLM will need to fall back on a more
prescriptive approach.
11.5
Plan Conformance
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Comment: Some comments requested
that 516 DM 11 direct the BLM offices
to reject proposals unless and until their
LUPs are updated to thoroughly address
potential environmental consequences.
Response: Section 11.5 clarifies the
requirement for conformance with
LUPs, including when a proposal may
be rejected.
11.6 Existing Documentation
(Determination of NEPA Adequacy)
Comment: Some comments suggest
that 516 DM 11 be revised to prescribe
a minimum level of interdisciplinary
review for completing a DNA.
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Response: Section 11.6 has been
revised to provide policy guidance on
the use of existing documentation.
Operational specifics on how to
implement the policy, such as levels of
interdisciplinary review, will be
provided in the BLM NEPA Handbook
(H–1790–1).
Comment: Some comments state that
the BLM DNA Worksheet does not meet
the requirements of NEPA compliance.
Response: In certain situations, the
BLM undertakes a DNA process to
review whether a proposed action has
already been fully analyzed in a NEPA
document. Where the proposed action
has not already been analyzed or where
it has been analyzed, but new
circumstances or information has come
to light, appropriate NEPA analysis and
documentation will be prepared.
Operational guidance on how to
implement this policy will be provided
in the BLM NEPA Handbook (H–1790–
1). The DNA Worksheet in appendix 1
and implementation-specific guidance
proposed in the January 25, 2006
Federal Register notice has been deleted
from 516 DM 11.
Comment: Some comments state that
using the DNA Worksheet process
provides the potential to overlook
environmental differences from widely
separated projects and to underestimate
the cumulative effects of nearby
projects.
Response: In accordance with 40 CFR
1502.9(c), section 11.6D states that if
existing NEPA documentation is
inadequate to cover the proposed action,
an appropriate level NEPA analysis
document will be prepared. The BLM
NEPA Handbook (H–1790–1) provides
guidance regarding consideration of
cumulative impacts when determining
whether a DNA can be used.
11.7 Actions Requiring an EA
Comment: Some comments expressed
confusion about the differences between
actions typically requiring an EA and
some of the same actions proposed in
the existing and new CXs.
Response: The January 25, 2006,
proposal included several editorial
errors in this sub-part. Sub-part 11.7C(1)
was revised for the sake of clarity.
11.8 Major Actions Requiring an EIS
Comment: Some comments requested
clarification of the term ‘‘highly
controversial’’ with regard to impacts in
sub-part 11.8A(1). The concern centered
on whether the term referred to matters
of public/political controversy versus
matters of scientific controversy.
Response: This sub-part has been
revised to remove the term ‘‘highly
controversial’’ as criteria for when an
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EIS is required. Guidance on how to
determine significance, including when
effects should be considered ‘‘highly
controversial’’ is applied in accordance
with CEQ regulations and requires
agencies to consider the degree to which
effects are likely to be controversial
when determining whether to prepare
an EIS. The BLM applies the ‘‘highly
controversial’’ concept to disagreements
about the nature of the effects.
Additional clarification and examples
will be provided in the BLM NEPA
Handbook (H–1790–1).
Comment: Some comments express
concern that the lists of actions that
typically require an EA or an EIS were
prescriptive, rather than discretionary,
and did not allow for any flexibility.
Response: Although 516 DM 11.7C
and 11.8A provide lists of actions
generally requiring EAs or EISs
respectively, 516 DM 11.7D, 11.7E and
11.8B specify the flexibility or
discretion allowed regarding the actions
on these lists, based on potential impact
significance.
11.9 Categorical Exclusions
Responses to section 11.9 comments
are divided into two blocks. Comments
of a general nature that may or may not
apply to more than one of the proposed
CXs are summarized and responded to
as ‘‘general comments.’’ Comments
specific to a proposed CX are
summarized and responded to in order
of category (e.g., B. Oil, Gas and
Geothermal; C. Forestry; D. Rangeland
Management; and so forth) as they occur
in 516 DM 11.
General Comments on Categorical
Exclusions
Comment: Some comments state that
the CX revisions are illegal; could short
circuit important safeguards;
circumvent existing laws, E.O., and the
BLM policies; violate the BLM’s
multiple use mission; and provide
insufficient protection despite the
application of ‘‘extraordinary
circumstances’’ (516 DM 2.3(A) and
appendix 2).
Response: The BLM disagrees. The
CEQ regulations (40 CFR 1508.4 and
1507.3) authorize Federal agencies to
establish and apply CXs. The BLM
followed CEQ regulations in proposing
additional CXs to reduce paperwork and
delays (40 CFR 1500.4 and 1500.5) and
enable the BLM to concentrate on
environmental issues that are associated
with proposed actions that require
further analysis in an EA or an EIS. Each
of the categories of actions in the new
CXs were subjected to an administrative
review. This review determined
whether there is sufficient supporting
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evidence, (based on past NEPA
analyses) and a review of actions to
support the finding that the activity
would not cause individually or
cumulatively significant environmental
impacts (https://www.blm.gov/planning/
news.html). When the CXs are used for
particular proposed actions, those
actions are reviewed to ensure that they
do not involve ‘‘extraordinary
circumstances’’ and are consistent with
all applicable laws for protection of the
environment. In addition, proposed
actions or activities must be, at a
minimum, consistent with the DOI and
the BLM regulations, manuals,
handbooks, policies, and applicable
LUPs regarding design features, best
management practices, terms and
conditions, and conditions of approval,
and stipulations. These reviews ensure
proper application of the CXs and act as
a ‘‘safeguard’’ (516 DM 2.3(A) and
appendix 2). Finally, some of the
information collected to prepare the CXs
was made available for public review
and comment available at https://
www.blm.gov/planning/news.html.
Additional information clarifying these
reports is now available at the same
Web site. The establishment and use of
CXs has been upheld in Heartwood, Inc.
v. U.S. Forest Service, 73 F. Supp. 2d
962, 972–73 (S.D. Ill. 1999), aff’d 230
F.3d 947, 954–55 (7th Cir. 2000).
Comment: Some comments indicate
support for the CX revisions and some
comments would like to expand the
categories of activities excluded from
further review under NEPA.
Response: The BLM will continue to
compile and review evidence to
determine if additional categories of
actions should be excluded from
additional NEPA review. The BLM may
propose additional CXs in the future.
Comment: Some comments state that
the BLM erroneously assumes that ‘‘the
only function of an EA is to determine
whether an EIS is needed.’’ Therefore,
‘‘any EA that resulted in a FONSI need
never have been prepared.’’
Response: The BLM disagrees. There
are three tasks served by completing an
EA as identified at 40 CFR 1508.9(a)(1)–
(3). The BLM analyzed past
environmental documents, including
EAs and FONSIs and the underlying
activities in establishing the CXs
described in this final action. Categories
of actions were considered eligible for
CXs when the EAs, FONSIs, and
subsequent review of these actions
showed no individually or cumulatively
significant impacts on the environment.
Comment: Some comments state an
opinion that the BLM should ban the
use of CXs.
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Response: The BLM disagrees. The
BLM establishes CXs in compliance
with the CEQ regulations implementing
the NEPA, particularly 40 CFR 1508.4
and 1507.3, which require agencies to
develop procedures for establishing CXs
for categories of actions that do not
normally require either an EA or an EIS.
The appropriate use of CXs also reduces
paperwork and delays (40 CFR 1500.4
and 1500.5), and enables the BLM to
concentrate on issues that are truly
significant and merit review in an EA or
EIS, rather than amassing needless
detail for actions demonstrated not to
have significant impacts (40 CFR
1500.1(b)).
Comment: Some comments, while
recognizing that the ‘‘extraordinary
circumstances’’ review is to occur before
an action is determined to be eligible for
use of a CX, express concern that the
BLM ‘‘often ‘defers’ special status
species and/or cultural resource
inventories on the sites of proposed
actions until after the NEPA process and
documentation is complete.’’ The
comments go on to question the BLM
practice of ‘‘add[ing] stipulations saying
that before any actual ground
disturbance occurs it will conduct the
required inventories and avoid any
identified resources.’’
Response: The BLM must comply
with the NEPA, as well as all applicable
environmental and resource protection
laws, such as the National Historic
Preservation Act, 16 U.S.C. 470 et seq.,
and the Endangered Species Act, 16
U.S.C. 1531 et seq. (ESA), before any
action is taken. Other than the broad
mandate of the Federal Land Policy and
Management Act, 43 U.S.C. 1701 et seq.,
which directs the BLM to prepare and
maintain an inventory of resource
values, there are no required
‘‘inventories.’’ Rather, the BLM has
discretion as to when and how to gather
information required to comply with
these statutes; that is, sufficient
information may come in different
forms, including but not limited to
inventories. In terms of applying the
CXs, the NEPA requires that the BLM
first determine whether any
extraordinary circumstances exist that
would preclude use of a CX. Several of
the extraordinary circumstances that the
BLM must consider directly address
resources mentioned in the comments.
For example, extraordinary
circumstances prohibiting the use of a
CX include instances where an
individual action may ‘‘have significant
impacts on such natural resources and
unique geographic characteristics as
historic or cultural resources’’ (516 DM
2 appendix 2(2.2)), ‘‘have significant
impacts on properties listed, or eligible
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for listing, on the National Register of
Historic Places as determined by either
the bureau or office’’ (516 DM 2,
appendix 2(2.7)), or ‘‘limit access to and
ceremonial use of Indian sacred sites on
federal lands by Indian religious
practitioners or significantly adversely
affect the physical integrity of such
sacred sites’’ (516 DM 2, appendix
2(2.11)). This means that the
Responsible Official must have
sufficient information regarding
‘‘cultural resources’’ to complete the
‘‘extraordinary circumstances’’ review
before a CX can be used to comply with
the NEPA.
Comment: Some comments state that
the BLM lacks the staff and funding for
appropriate monitoring of categorically
excluded activities. Some comments
express concern that by categorically
excluding more activities, there will be
insufficient data to analyze the impacts
of these activities. Other comments ask
the BLM to assure the public that
impacts from the implementation of
categorically excluded activities be
monitored.
Response: An activity that is subject
to a CX by definition is an activity that
is within a category of actions that have
previously been found not to have
significant impacts, either individually
or cumulatively. That being said,
regardless of whether a proposed
activity is reviewed under an EA, EIS or
CX, the BLM monitors the effects of
these activities to the extent its budget
allows. The BLM’s program
management and associated staffing
decisions regarding the monitoring of
effects are subject to the appropriations
process. (See, Anti-Deficiency Act, 31
U.S.C. 1341).
Comment: Some comments state that
the BLM should increase public
notification of CX decisions made.
Response: The CEQ regulations (40
CFR 1506.6) require public notice about
the completion of NEPA analysis under
certain circumstances. These regulations
do not require public notification of the
use of a CX. Some BLM offices currently
support Web sites that list the decisions
made in their management area,
including the NEPA documents
associated with those decisions
(including applying a CX). For example,
see the Utah State Office Environmental
Notification Bulletin Board at https://
www.ut.blm.gov/enbb/index.php.
Comment: Some comments state that
the BLM should include the CXs from
the Energy Policy Act of 2005 in the 516
DM 11 revisions.
Response: The CXs included in the
Energy Policy Act of 2005 are statutory
CXs; therefore, do not need to be listed
in 516 DM 11.
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Comment: Some comments ask the
BLM to describe how cumulative
impacts of the proposed CX activities
would be evaluated. Some comments
suggest that 516 DM 11 be revised to
ensure that the cumulative impacts of
projects covered by a CX are analyzed.
Response: An action can only be
categorically excluded from further
NEPA analysis when it has been shown
that the action fits within a category of
actions that has already been
determined not to have a significant
environmental effect on the human
environment, individually or
cumulatively (see 40 CFR 1508.4). For
all of the categories of actions for which
the CXs were proposed, the analysis of
the NEPA documents prepared for such
actions, as well as subsequent
evaluations of the effects of the actions,
showed that the actions did not cause
significant effects. Further, when
considering whether to use a CX, one of
the ‘‘extraordinary circumstances’’ that
must be evaluated is whether the
proposed action may ‘‘have a direct
relationship to other actions with
individually insignificant but
cumulatively significant environmental
effects’’ (516 DM 2.3(A)3 and appendix
2 (2.6)). If it might, then an EA or an EIS
must be completed for the action, and
a CX cannot be applied.
Comment: Some comments ask the
BLM to evaluate the cumulative impacts
of the proposed CXs, the revisions to the
Northwest Forest Plan’s (NWFP) Survey
and Management Program and Aquatic
Conservation Strategy; the National
Forest Management Act Planning
regulations; and the National Forest
Management Act notices, comment, and
appeal regulations.
Response: The new or modified CXs
are specific to a revision of the
procedures described in the 516 DM 11
for implementing the NEPA within the
BLM. The determination that
establishing CXs does not require NEPA
analysis and documentation has been
upheld in Heartwood, Inc. v. U.S. Forest
Service, 73 F. Supp. 2d 962, 972–73
(S.D. Ill. 1999), aff’d 230 F.3d 947, 954–
55 (7th Cir. 2000) (holding creation of
CXs to be an establishment of agency
procedure for which CEQ regulations do
not require preparation of an EA or EIS).
The CXs proposed in January 2006 and
finalized here are part of the BLM’s
effort to update internal NEPA
implementing procedures. A cumulative
effects analysis of the establishment of
these CXs, in relation to the NWFP, the
National Forest Management Act
Planning regulations, and the National
Forest Management Act is not
appropriate in this context. However, in
developing the Forestry CXs, the BLM
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reviewed past actions and associated
NEPA documents. These NEPA
documents included analyses of
cumulative effects, which in relevant
instances, included actions taken by the
Forest Service. The BLM’s review of
these past actions, the NEPA analyses
specific to the actions, and anticipated
effects, as well as the actions’ actual
effects, allowed the BLM to determine
that the actions had no individual or
cumulative significant impacts, and that
development of a CX covering such
actions was warranted. The final
determination whether a specific
proposed action will have a significant
cumulative effect or not, is completed at
the time the specific proposal is
reviewed by considering the
applicability of any extraordinary
circumstances.
Comment: Some comments state that
the BLM needs to ensure that
implementation of all the CXs will not
cumulatively result in jeopardy to listed
endangered species.
Response: The Responsible Official
must ensure that no BLM action will
jeopardize a listed species under the
ESA. Before a CX can be used, the
Responsible Official must determine
that no ‘‘extraordinary circumstances’’
apply. If ‘‘extraordinary circumstances’’
(516 DM 2.3(A)3 and appendix 2 (2.8)),
which addresses endangered species,
applies, a CX may not be used.
Responses to Specific Comments on
Section 11.9—Categorical Exclusions
B. Oil, Gas, and Geothermal Energy
(Sub-parts B(6)–(8))
B(6)—Comments.
Comment: Some comments state that
the proposed CX 11.9B(6) should not be
implemented because geophysical
operations were excluded when
Congress authorized additional energy
development-related CXs under the
Energy Policy Act of 2005.
Response: Section 390 of the Energy
Policy Act of 2005 does not provide for
a CX for the geophysical activities
described in the proposed CXs. The Act
does not preclude the appropriate
exercise of authority to administratively
establish CXs in accordance with the
NEPA, the CEQ regulations, and the DOI
and the BLM NEPA procedures.
Comment: Some comments state that
the proposed CX 11.9B(6) is a policy
change aimed specifically at benefiting
the oil and gas industry and that as
such, is a ‘‘scheme’’ to make energy
exploration companies more money.
Response: No change to the CX was
requested by these comments, no
changes were made in response. The
BLM proposed CX 11.9B(6) because
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CEQ implementing regulations (40 CFR
1509.4 and 1507.3) allow federal
agencies to identify categories of
actions, which normally do not require
either an EA or an EIS. The
development of this CX was based on
generally accepted analytical
procedures, which included completion
of a census of available data on
geophysical exploration. See https://
www.blm.gov/planning/news.html. One
benefit to all stakeholders of adopting
new CXs for activities, which have been
shown to have no individually or
cumulatively significant effects, is
additional federal resources can be
redirected to analyzing and mitigating
activities likely to have significant
adverse environmental consequences.
Comment: Some comments suggest
that the proposed CX 11.9B(6) would
promote the segmentation of a major
project into several categorically
excluded small projects, which would
prevent appropriate consideration of
cumulative impacts.
Response: The BLM disagrees.
Geophysical exploration activities are
independent actions and not connected
actions as defined in NEPA (40 CFR
1508.25 (a)(1)). Geophysical exploration
activities are data collection activities
used to gather information that may be
used to inform future decision-making
regarding oil, gas or geothermal
development proposals by providing
information on the location of energy
resources. It is not a forgone conclusion
that the energy resources identified
through this data collection will
actually be developed. Before a CX can
be used, a proposed action must be
reviewed to determine whether or not
any of the ‘‘extraordinary circumstance’’
(516 DM 2.3(A)3 and appendix 2),
applies. In particular, ‘‘extraordinary
circumstance’’ 2.6 addresses the
potential for significant cumulative
impacts; if it does apply, the CX cannot
be used.
Comment: Some comments state that
federal court and administrative
decisions have either remanded the
BLM decisions to approve geophysical
exploration or affirmed agency
decisions, only after the BLM proposed
additional mitigation measures.
Response: The data analyzed and
reviewed by the BLM validate the
assertion that the impacts from
geophysical operations would not be
significant. Specific to the comment
related to litigation, the data indicate
that out of 244 projects reviewed, the
NEPA analyses of eight geophysical
exploration projects, supported by EAs,
were challenged through administrative
appeals or litigation. Only two of the
eight were remanded to the BLM. In one
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situation, the NEPA document was
found inadequate where the BLM failed
to consider reasonable alternatives (such
as limiting use to existing roads) that
had been suggested, and in the other,
the BLM failed to provide a comment
period that had been promised and that
the court found to be appropriate under
the circumstances of that case. Neither
was due to a finding of significant
impacts associated with geophysical
exploration. Geophysical exploration
(the impacts from those activities and
how the BLM field personnel address
the approval process) has changed over
the last several years. There have been
lessons learned from the results of this
litigation, from personal observation by
field staff associated with the projects,
field data collection through
monitoring, and systematic evaluation
of information received from the
proponents. Accumulation of
professional knowledge resulted in
design features that previously were not
part of proponent geophysical
proposals, yet are now considered
routine. Proponents either with or
without the BLM consultation now
incorporate best management practices
into proposals. Project design features
are site specific to the local concerns
and resource values. They represent a
commonality of best management
practices that are integral to the project
being authorized. Field personnel that
routinely permit these actions know the
needs based on accumulated
professional knowledge of resource
concerns in the area at issue, and either
assure these aspects appear in the
proponent’s proposal or include them as
conditions of approval in the
authorization. ‘‘Conditions of approval’’
or ‘‘terms and conditions’’ are terms of
art that represent the practices and
standards that are routinely applied to
geophysical projects specific for that
particular office. Their application does
not require a new analysis each time a
project is submitted, but results in a list
of measures that the proponent must
implement based on local conditions. In
all cases, proposed actions or activities
must be, at a minimum, consistent with
the DOI and the BLM regulations,
manuals, handbooks, policies, and
applicable LUPs regarding design
features, best management practices,
terms and conditions, conditions of
approval, and stipulations. Also
associated with this improved
professional knowledge base, of the
BLM field experience, has been the
steady improvement of geophysical
techniques and best management
practices by the geophysical industry.
Low impact techniques have allowed for
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substantial reductions in the amount of
actual surface disturbance and
associated resource impacts. Physical
impacts such as road construction are
rare and the impacts to soil or
vegetation resources are minimal or
short-term.
Comment: Some comments state that
geophysical exploration activities cause
‘‘disturbance’’ and related erosion
impacts, such as landslides and slumps.
Therefore, they recommend that the CX
not be adopted.
Response: Available data supports
adoption of the CX. The CX 11.9B(6)
was established after careful review of
244 geophysical exploration projects
previously approved by the BLM. The
data examined for these projects
included project-specific information on
the location, the type of NEPA review
performed, predicted environmental
impacts of proposed actions, and actual
environmental impacts after the action
was completed. No projects were shown
to have significant impacts, individually
or cumulatively. According to the
review of the NEPA analysis completed
for these 244 geophysical exploration
projects, including review of the effects
of the completed projects themselves,
predicted significant impacts, including
erosion-related impacts as a result of
geophysical exploration, did not occur.
In addition, with respect to the
resources mentioned in the comments,
the BLM applies specific ‘‘Terms and
Conditions’’—as indicated in number
seven of the BLM Form 3150–4 and
requires suspension of operations when
unnecessary disturbance to soils may
occur. This term and condition is a part
of all geophysical Notices of Intent (see
the BLM Form 3150–4). In addition, if
the required ‘‘extraordinary
circumstances’’ review conducted for
any proposed action indicated such
impacts as ‘‘landslides’’ and ‘‘slumps’’
might be significant, the CX would not
be used.
Comment: Some comments state that
the use of the geophysical exploration
CX would have negative impacts on
non-commercial uses, such as scientific,
educational, recreational, aesthetic, and
spiritual purposes.
Response: See response above. The
BLM reviewed 244 geophysical
exploration projects. None of the
projects reviewed during the
establishment of this CX resulted in a
significant impact, either individually
or cumulatively. In addition, the BLM
will review all future projects against
the DOI’s ‘‘extraordinary
circumstances.’’ If the review indicates
that the action may have a direct
relationship to other actions with
individually insignificant, but
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45511
cumulatively significant environmental
effects (i.e., to non-commercial uses,
such as scientific, educational,
recreational, aesthetic and spiritual
purposes), the CX cannot be used.
Comment: Some comments state that
geophysical (e.g. seismic) exploration
activities have potentially significant
impacts to environmental and cultural
resources.
Response: None of the 244
geophysical exploration projects
reviewed during the establishment of
this CX resulted in a significant impact,
either individually or cumulatively.
Further, the BLM believes the
established permitting process ensures
that if there are potential individually or
cumulatively significant environmental
effects, an EA or EIS, as appropriate,
would be done. Included in the
permitting process is the requirement to
review the DOI list of ‘‘extraordinary
circumstances’’ (516 DM 2.3A(3) &
appendix 2) for every proposed action.
‘‘Cultural resources’’ are specifically
provided for in this list. If the required
‘‘extraordinary circumstances’’ review
indicated that significant impacts to
environmental or cultural resources
might occur, the CX would not be used.
Further, the use of the CX during the
NEPA review process does not eliminate
the need to comply with Section 106 of
the National Historical Preservation Act
(Pub. L. 89–665) or the Archeological
Resources Protection Act (Pub. L. 96–
95), or any other applicable resource
protection law.
Comment: Some comments express
concern that geophysical exploration
activities can damage roadless areas by
creating noticeable vehicle routes,
which can attract traffic by
‘‘unauthorized’’ off-highway vehicle
drivers.
Response: Historically, older
geophysical exploration operations
required the use of some type of road
construction. These operations left
travelways that would take time to
completely reclaim. In the interim, these
routes would remain visible and may
have encouraged off-highway travel by
some members of the public. Best
management practices over time have
reduced the visibility of noticeable
vehicle tracks through project design
features so that non-authorized use is
discouraged. Further, the proposed CX
was specifically limited to geophysical
exploration projects that do not involve
road construction. The BLM reviewed
244 geophysical exploration projects
during the establishment of this CX.
None of the projects resulted in a
significant impact, either individually
or cumulatively. As an additional
limitation, the BLM has added a
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requirement to this CX that when road
construction is involved, the CX would
not be used and additional NEPA
review would be completed. Further,
the proposed geophysical exploration
activities can only proceed using this
CX where none of the ‘‘extraordinary
circumstances’’ apply (516 DM 2.3A(3)
& appendix 2).
Comment: Some comments state that
the proposed CX 11.9B(6) would
‘‘wrongly exclude’’ the covered actions
from compliance with federal laws
protecting wildlife, such as the ESA.
Response: The use of a CX does not
eliminate the need to comply with
Section 7 of the ESA or other federal
laws. None of the 244 projects reviewed
during the establishment of this CX
resulted in a significant impact, either
individually or cumulatively. Further, if
the proposed geophysical exploration
activity has the potential to significantly
impact listed threatened or endangered
species, or their critical habitat,
‘‘extraordinary circumstance’’ 2.8 (516
DM 2 appendix 2.8) applies, and an EA
or EIS, as appropriate, is required.
Comment: Some comments state that
weed invasion follows the network of
seismic activities across the landscape,
which can result in irreversible weed
invasions that radically alter fire cycles
and endanger wildlife habitat.
Response: None of the 244 projects
reviewed during the establishment of
this CX resulted in a significant impact,
either individually or cumulatively. In
addition, specific to the resource
commented on, if the proposed
geophysical exploration action may
contribute to the introduction,
continued existence, or spread of
noxious weeds, ‘‘extraordinary
circumstance’’ 2.12 (516 DM 2,
appendix 2.12) would eliminate the
decision-maker’s ability to use CX
11.9B(6). An EA or EIS, as appropriate,
would be required.
Comment: Some comments ask the
BLM to revise the proposed geophysical
exploration CX 11.9B(6) to prohibit
seismic activity during migratory bird
breeding season.
Response: None of the 244 projects
reviewed during the establishment of
this CX resulted in a significant impact,
either individually or cumulatively. In
addition, the DOI and the BLM use a
NEPA review process that ensures that
if any of the ‘‘extraordinary
circumstances,’’ as defined in 516 DM
2.3A(3) and appendix 2, apply, a CX
cannot be used. ‘‘Extraordinary
circumstance’’ 2.2 (516 DM 2 appendix
2) affords protection specifically for
migratory birds. Therefore, if a project
design feature intended to provide
protection of migratory bird breeding
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activities in an area occupied by these
birds were to be refused by the
applicant, or if its efficacy has not been
sufficiently assured, an EA or EIS, as
appropriate, would be required.
Proposed actions or activities must be,
at a minimum, (as is stated in the
preamble to this section) consistent with
Laws (such as the Migratory Bird Treaty
Act (Pub. L. 86–732), DOI and BLM
regulations, manuals, handbooks,
policies, and applicable LUPs regarding
design features, best management
practices, terms and conditions,
conditions of approval, and stipulations.
Comment: Some comments ask the
BLM to revise the proposed geophysical
exploration CX 11.9B(6) to ensure that
operations do not result in cumulative
impacts.
Response: An activity that is subject
to a CX by definition is an activity that
has been found not to have significant
impacts, individually or cumulatively.
Geophysical exploration activities that
would be authorized under the CX have
been shown not to have significant
impacts, either individually or
cumulatively based upon the BLM
administrative review of 244
geophysical exploration projects. The
analysis report is available at the BLM
Web site at https://www.blm.gov/
planning/news.html. None of the NEPA
documentation for the 244 geophysical
exploration projects analyzed in the
study during the establishment of the
CX indicates the occurrence of
significant impacts. The BLM also
employs a NEPA review process that
ensures, if any of the ‘‘extraordinary
circumstances,’’ as defined in 516 DM
2.3A(3) and appendix 2, apply, a CX
cannot be used. One of these
‘‘extraordinary circumstances’’ that
precludes the use of a CX addresses
cumulative impacts.
Comment: Some comments state that
establishment of terms and conditions
for specific proposed actions depends
on the soil, weather, ground cover, and
type of machinery to be used in each
case; therefore, the proposed CX would
not adequately account for these sitespecific issues.
Response: The BLM agrees that the
design of each proposed action depends
on soil, weather, ground cover, and type
of machinery to be used; however, as
proposed actions are designed and then
reviewed against the CX list, such
actions or activities must be, at a
minimum, consistent with the DOI and
the BLM regulations, manuals,
handbooks, policies, and applicable
LUPs regarding design features, best
management practices, terms and
conditions, conditions of approval, and
stipulations. The geophysical
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exploration techniques, impacts
resulting from the techniques, and the
BLM’s field personnel knowledge and
experience in reducing impacts from
this type of activity have improved over
time. The lessons learned based on
personal observation by field staff
associated with the projects, field data
collection through monitoring, and
systematic evaluation of information
received from the proponents has
resulted in accumulation of professional
knowledge that has led to development
of design features that were not
previously part of proponent
geophysical proposals. Use of design
features to minimize impacts to soil and
ground cover are now routinely
included based on local conditions. The
BLM alerts proponents regarding
resource values of concern in a given
area, and proponents incorporate best
management practices into the proposal
so that impacts are now minimal. In
addition, the BLM’s review of 244
projects determined that there is no
significant impact from this activity.
Further, each proposed action is
reviewed against the DOI’s
‘‘extraordinary circumstances’’ as
described in 516 DM 2.3A(3) and
appendix 2. Any proposed geophysical
exploration activity that does not satisfy
these requirements must be analyzed
through the EA or EIS process, as
appropriate.
B(7) & (8)—Comments.
Comment: Several comments were
received related to proposed CXs 11.9
B(7) for permitting infill wells within
the [reasonable foreseeable
development] RFD for an established
geothermal field, and B(8) for the
issuance of site licenses to operate
geothermal facilities whose construction
and operation were included in a
utilization plan NEPA document.
Comments addressed such concerns as
the potential for geothermal activity to
affect water-confining soil layers and
potentially result in the loss of wetted
playa areas; impacts on special-status
species and endangered species and
their habitats that may result from use
of the proposed CXs; and currency of
LUPs with respect to the ecological
status of lands and waters under
discussion. Some commenters sought to
expand the use of these CXs beyond the
State of Nevada; they felt that Nevada
should not be granted special
consideration over other states and
asserted that projects in other states
could meet the same criteria as used in
Nevada. Commenters also asked why
there was a need for further NEPA
analysis, rather than a DNA, where the
NEPA document for the field
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development or the utilization plan
included the activities proposed for
Geothermal CX 11.9 B(7). In addition,
comments expressed interest in
clarification of what actions CX 11.9
B(8) was intended to cover, and what
actions would be covered by methods of
complying with the NEPA.
Response: Upon review of the BLM’s
NEPA compliance procedures, in
general, and in consultation with CEQ,
the BLM has decided not to finalize
proposed CXs 11.9B(7) and 11.9B(8). As
explained above in the description of
modifications made from the January
2006 proposal, the BLM has determined
first that, regarding B(7) (infill wells), a
DNA combined with more focused
development-stage NEPA documents
should normally suffice for NEPA
compliance, as some commenters
suggested, and second, that a CX (or an
EA) for B(8) is redundant and thus
unnecessary because no new
environmental impacts result from the
administrative/ministerial action of
issuing a site license where operation of
the plant was already covered in the
NEPA analysis and documentation
prepared for the utilization plan. Both of
these solutions are applicable
nationwide. To the extent that
comments express concern regarding
particular resources, the method an
agency uses to fulfill its NEPA
obligations is distinct from the agency’s
continuing obligation to comply with
other environmental protection statutes
such as the Clean Water Act, 33 U.S.C.
1251 et seq., the Endangered Species
Act, 16 U.S.C. 1531 et seq. (special
status species are addressed as part of
the BLM’s conservation plans under
Section 2 of the Endangered Species
Act), and the Federal Land Policy and
Management Act, 43 U.S.C. 1701 et seq.
(land use planning). The BLM LUPs are
routinely evaluated to determine
whether the LUP decisions and NEPA
analysis are still valid. All actions,
including those categories of actions
considered here, must be consistent
with an approved LUP. Regardless of
the age of the LUP(s) affected, each
proposed action would also be
evaluated on its own merits, and
updated information provided as
necessary in the more site- and/or more
project-specific NEPA analysis. In most
cases, for instance, the initial
development plans for the types of
actions contemplated here would have
already been analyzed in a project-level
NEPA document in addition to the LUP.
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Responses to Specific Comments on
Section 11.9—Categorical Exclusions
C. Forestry (Sub-Parts C(6)–(9))
Broad Concerns That Apply to the New
Forestry CXs
Comment: Some comments state that
the proposed Forestry CX parameters
are inadequate to protect elements of the
environment, specifically predatory bird
nesting sites, woodpecker habitat, soils
compaction, weed dispersal, small
mammal burrows, and surface water
quality.
Response: The BLM analysis available
at https://www.blm.gov/planning/
news.html demonstrates this is not the
case. Three of the four proposed
Forestry CXs, 11.9C(7)–(9), are based on
three U.S. Department of Agriculture
Forest Service (FS) CXs, their
supporting data, and an analysis by the
BLM demonstrating that such proposed
actions and their environmental effects
are comparable when the action is taken
by the BLM. The FS considered the
potential for significant effects during
the NEPA review process (68 FR 44598–
44608, July 29, 2003). Based on
assessments of local wildlife habitat
conditions after the actions were taken,
no significant cumulative effects were
observed by the FS. A few of the
projects reviewed resulted in minor soil
disturbance and compaction, and a few
others showed that small numbers of
noxious weeds or invasive plants
entered the area where the trees had
been removed. The FS subject-matter
specialists and Responsible Officials
found that these impacts were within
forest plan standards and were not
significant in the NEPA context (40 CFR
1508.27). Based upon the comparison
between the FS and the BLM lands,
policies, and business practices as
outlined in the BLM analysis, the BLM
actions are not expected to result in
significant introductions, continued
existence, or spread of noxious weeds or
non-native invasive species. In addition,
when applying the CXs to the BLM
lands, the BLM only considers use of
the CXs when there are no
‘‘extraordinary circumstances’’ (516 DM
2.3A(3) and appendix 2.12), which will
cause individually or cumulatively
significant impacts on the human
environment.
The fourth proposed CX 11.9C(6),
which addresses sample tree felling
(STF) to gather net timber volume data,
is based on a 100 percent census of STF
surveys conducted in five BLM
management districts in western Oregon
from October 1, 2001, through
September 30, 2005. These five Districts
(Coos Bay, Eugene, Medford, Roseburg,
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and Salem) wrote EAs for the timber
sales that were associated with the 59
STFs performed. The EAs addressed a
range of environmental impacts for the
five districts including the types
mentioned in the comments. The STF
business practices and skills of those
conducting the action on lands similar
to the original five Districts are the
same. The BLM believes there are
sufficient data to show that no
individually or cumulatively significant
environmental effects were predicted or
occurred as a result of the 59 STF
surveys, and therefore the BLM is
confident that no individually or
cumulatively significant environmental
effects will occur due to future STF
actions within the Districts identified.
The Lakeview District Klamath Field
Office was inadvertently left out of the
area of coverage of the proposed CX, but
has been added to the revised CX
proposal. Actions in the Klamath Field
Office are the same as those taken in the
five Districts identified above and result
in the same non-significant
environmental effects. In addition,
proposed actions in the Klamath Field
Office will also be subject to the
‘‘extraordinary circumstances’’ test, and
are expected to have no significant
environmental effects.
Comment: Some comments state that
the BLM does not disclose that ‘‘it is in
the process of implementing several
internal and administrative regulatory
changes that, in addition to the
proposed small timber harvest [CXs
(11.9C(7)–(9)], will have a cumulative
effect on the environment that has not
been analyzed as required by law.’’ The
‘‘internal and administrative regulatory
changes’’ the comments refer to are the
NWFP, the National Forest Management
Act Planning regulations and the
National Forest Management Act.
Response: The BLM disagrees with
the comments, and believes that it is
following CEQ guidelines by notifying
the public on proposed changes to the
516 DM 11 (See 71 FR 4159–4167,
January 25, 2006; see also https://
www.blm.gov/planning/news.html). The
new forestry CXs are specific to the
DOI’s 516 DM 11 for implementing
NEPA within the BLM. A cumulative
impacts evaluation in relation to the
referenced ‘‘changes’’ is not appropriate,
since there is no effect on the
environment by this administrative
change. The proposed CXs are part of
the BLM’s effort to update internal
NEPA implementing procedures. The
establishment of CXs, as internal agency
procedures for implementing the NEPA,
has been held not to require the
preparation of an EA or an EIS, under
the CEQ regulations, see Heartwood,
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Inc. v. U.S. Forest Service, 73 F. Supp.
2d 962, 972–73 (S.D. Ill. 1999), aff’d 230
F.3d 947, 954–55 (7th Cir. 2000). The
final determination on whether a
specific proposed forestry-related action
will have a significant cumulative effect,
is completed at the time the proposal is
reviewed and evaluated using the
‘‘extraordinary circumstances’’ test, or if
necessary, through an EA or EIS.
Comment: Some comments state that
the forestry activities proposed for CX
process review are ‘‘beyond the
intended scope and purpose of the
categorical exclusion clause’’ in NEPA;
and by ‘‘exempting such activities, the
BLM is essentially advocating that
actions with significant environmental
impacts escape close scrutiny under the
requirements of NEPA.’’
Response: The BLM disagrees that
using a categorical exclusion allows
actions with significant environmental
impacts to escape scrutiny. To avoid
repetitive documentation of known nonsignificant effects, the CEQ regulations
(40 CFR 1500.4(p), 1507.3 and 1508.4;
also see CEQ’s testimony before the
House Committee on Resources Task
Force on Updating the NEPA Lessons
Learned Oversight Hearing on
November 17, 2005), provide for
defining ‘‘categories of activities’’ whose
effects do not normally require review
in an EA or an EIS. The process of
defining these categories is an integral
part of the NEPA regulatory framework.
In this case, the BLM collected data on
the NEPA analyses used for sample tree
felling (CX 11.9C(6)). The BLM analyzed
the NEPA review activities documented
by the FS related to live tree harvests,
salvage tree harvesting, and sanitation
harvesting projects. The BLM and the
FS data and analysis support a
determination that (1) the proposed
Forestry CX activities do not have
significant effect(s) on the human
environment, and (2) these CXs meet the
intent of the CEQ regulations that
govern the establishment of CXs. The
BLM is establishing these categories of
Forestry activities because the
appropriate implementation of the
NEPA requires concentrating agency
analysis efforts on major federal actions
and not expending scarce resources
analyzing agency actions where
experience has demonstrated the
insignificance of predictable effects.
Comment: Some comments state that
the new live tree harvest, salvage tree
harvesting, and sanitation harvest CXs
11.9C(7)–(9) will, when combined with
new opportunities for energy
development, affect available open
space and could be ‘‘devastating to the
environment,’’ specifically air and water
quality, wildlife, and tourism.
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Response: The BLM disagrees that the
use of CXs 11.9C(7)–(9) will affect
available open space, or be
‘‘devastating’’ to the environment and
tourism. As discussed above, the BLM
analyzed the FS information and
determined the BLM forestry activities
included in the CXs and their effects are
comparable. The FS reviewed activities
related to live tree harvests, salvage tree
harvesting, and sanitation harvesting
projects, and determined that the
proposed CXs do not have significant
effects on the human environment,
including air and water quality and
wildlife. Further, if there are
‘‘extraordinary circumstances’’ listed in
516 DM 2, appendix 2 that apply, the
Responsible Official cannot use the new
forestry CXs. The use of the CX does not
eliminate the need to comply with other
applicable resource protection laws. The
BLM will determine whether a specific
proposed Forestry-related action will
have a significant cumulative effect on
the environment, including wildlife and
tourism values, at the time the proposal
is reviewed using the extraordinary
circumstances test. If the proposal does
not pass the extraordinary
circumstances review, an EA or an EIS
will be completed.
Comment: Some comments state that
tree harvesting is ‘‘never completely
uncontroversial, and it often imposes
significant impacts on the terrestrial and
aquatic ecosystems of the area.’’ The
comments further state that a CX that
enables tree harvesting for any reason
provides insufficient opportunity for
public review.
Response: Based on the BLM’s
reviews of the FS tree harvesting
projects, the BLM determined that
similar projects would have similar
effects on the BLM land, and would
have no significant effects on the
terrestrial and aquatic ecosystems in the
area of the projects. In the development
of the three harvesting and salvaging
CXs, the FS reviewed the effects of 154
tree harvesting projects across the
country, with actions similar to those
allowed in the three categories (See
https://www.fs.fed.us/emc/nepa/library/
20030108_fr_notice.pdf). Prior to
implementation, none of the projects
reviewed predicted significant effects on
the human environment. After
implementation, on-site reviews of
environmental effects of these projects
were conducted by interdisciplinary
teams of resource specialists. The
reviews by the BLM concluded that
none of the projects had a significant
effect on the human environment. In
addition, the BLM applies the review of
extraordinary circumstances to projects,
including whether an action has highly
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controversial environmental effects or
involves unresolved conflicts
concerning alternative uses of available
resources. If one or more of the
extraordinary circumstances listed in
516 DM 2, appendix 2.3 apply, the
Responsible Official cannot use the new
forestry CXs. Applying a CX to a
proposed action does not preclude
public involvement with the proposal.
Interested publics will be involved as
appropriate throughout the decisionmaking process. The type and level of
public involvement should be
commensurate with the decision at
hand. Forest management decisions,
including those where a CX is applied,
are protestable under 43 CFR 5003.3.
Comment: Some comments state that
using the FS data to justify the proposed
BLM live tree harvest, salvage tree
harvesting, and sanitation harvesting
activities CXs 11.9C(7)–(9) is
inappropriate because the FS lands and
projects in ‘‘different regions may not be
comparable for a variety of reasons.’’
Response: The data is applicable to
the BLM lands because forestry related
projects and their predictable
environmental impacts are substantially
the same on the BLM and the FS
administered public lands as
demonstrated by the comparability
analysis conducted by the BLM
(https://www.blm.gov/planning/
handouts/CX_Report-ForestryFS_CXs.pdf). Laws governing forest
management for the BLM and the FS are
very similar. While the agencies have
separate enabling legislation, both
require that forest lands be managed
according to sustained-yield and
multiple-use principles. As part of land
management, the agencies are further
mandated to meet the requirements of
environmental laws including the Clean
Water Act, Clean Air Act, Endangered
Species Act, and the National Historic
Preservation Act when making
decisions. Finally, the proposed actions
designed and reviewed for application
of a CX must be, at a minimum,
consistent with DOI and BLM
regulations, manuals, handbooks,
policies, and applicable LUPs regarding
design features, best management
practices, terms and conditions,
conditions of approval, and stipulations.
Comment: Some comments state that
standing dead trees (snags) and dying
trees ‘‘play an important ecosystem
role’’ that is ‘‘highly valued’’ and
‘‘under represented.’’ Some comments
state that the BLM and the FS policies
for conserving snags do not reflect an
adequate appreciation of the current
state of knowledge about their
ecological value. Still other comments
want the BLM to develop ‘‘snag
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retention guidelines for each
physiographic province * * *’’ They
state that until this is done, the BLM
should not allow any snag larger than 20
inches diameter at breast height (dbh) to
be removed based on a report prepared
for the DOI Final Draft Recovery Plan
for the Northern Spotted Owl issued
in1992.
Response: The BLM agrees that
standing dead and down woody
material is an important component of
a healthy forest ecosystem. The BLM’s
LUPs in the Pacific Northwest are based
on the Record of Decision for
Amendments to Forest Service and
Bureau of Land Management Planning
Documents Within the Range of the
Northern Spotted Owl (ROD) and
Standards and Guidelines for
Management of Habitat for LateSuccessional and Old-Growth Forest
Related Species Within the Range of the
Northern Spotted Owl (S&G), April
1994. The Final Draft Recovery Plan for
the Northern Spotted Owl (1992),
referenced by the commenters, was
considered when writing the Final
Supplemental EIS and Record of
Decision (ROD) (page 17). The S&G
addressed physiographic provinces
(Introduction page A–3) and both the
retention and removal of snags (S&G,
pages C–14, 15). The ROD and S&G do
not set a diameter limit on snag
retention. Since the BLM LUPs are
based on the ROD and S&G, the BLM
rejects setting an arbitrary limit of 20
inches dbh on snag retention.
Comment: Some comments express
preference for a 100 or 250-acre upper
size limit on the new forestry CXs
11.9C(7)–(9) while others ask that the
upper limit be reduced to 10 acres for
all potentially eligible harvest activities.
Some comments state that establishing
‘‘a higher [acres] limit for salvage and
insect/disease timber sales makes
absolutely no sense’’ and that ‘‘allowing
commercial projects to be included
heightens [environmental] risk * * *.’’
Response: The BLM is finalizing the
proposed CX language as written. The
BLM analyzed the FS data, and
determined that the FS size acres limits,
which are based on their data, are
appropriate for the CXs. Having the
BLM and the FS using the same size
limits for similar treatments will help
maintain consistency between the
agencies. The BLM would need to
gather new data to support using a CX
for larger treatment areas. The BLM’s
CXs 11.9C(7)–(9) are similar to three FS
forestry CXs formally adopted in 2003
(68 FR 44598–44608, July 29, 2003). The
FS instituted their forestry CXs (Forest
Service Handbook (FSH) 1909.15, Ch.
31.2(12–14)) based on 154 completed FS
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projects that had sufficient NEPA
analysis documentation. The FS data
show that no individually or
cumulatively significant effects resulted
when the activities described in the
three FS forestry CXs were used. Since
no significant effects occurred at the
current size limits, there is no logical
reason to arbitrarily reduce the size
limits. For additional information on the
FS data collection and analysis process
and the method used to determine
reasonable project area limits, refer to 68
FR 44598–44608, July 29, 2003, and
supporting documents and the BLM
analysis at https://www.blm.gov/
planning/handouts/CX_Report-ForestryFS_CXs.pdf. The BLM also rejects the
notion that allowing commercial use of
the harvest material increases
environmental risks. The effects on the
ground of a project would be the same
regardless of whether or not someone is
likely to profit from the venture.
Comment: CXs 11.9C(7)–(9) provide
for ‘‘temporary road construction.’’
Some comments ask the BLM to define
‘‘temporary road’’ and other comments
ask the BLM to clearly define what
constitutes temporary road construction
to ‘‘minimize impacts.’’ Some comments
state that limiting temporary road
construction to ‘‘no more than 0.5
mile[s]’’ is too constraining, while
others state that any road building
causes significant environmental
impacts.
Response: The BLM agrees that it
needs a definition for temporary roads.
For use of the specific forestry CXs
11.9C(7)–(9) the BLM has rewritten the
CXs to define temporary roads based on
the definitions in the FS regulations,
which will meet the BLM needs and
ensure compatibility between agencies
for these specific CXs. The BLM rejects
the notion that any road construction
causes significant environmental
impacts. The BLM reviewed the FS data
where 35 of the 154 timber sales
reviewed by the FS required temporary
road construction. The FS found no
significant effects in reviewing these
projects. The average length of
temporary road construction for the 35
sales was 0.5 mile. Based upon its
analysis, the BLM determined that
temporary road construction when the
CX criteria are met will be nonsignificant. Therefore, it is appropriate
to use the 0.5-mile maximum length
limit for temporary road construction
for these CXs, to maintain consistency
between agencies.
Comment: Some comments state that
the BLM should conduct an in-depth
cost-benefit analysis of the proposed
forestry CXs: 11.9C(6)–(9).
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Response: A forestry cost-benefit
analysis of each CX is not necessary
because the BLM determined that the
cumulative economic impact of the
proposed changes to 516 DM 11,
including adoption of CXs 11.9C(7)–(9)
would not have an annual effect of $100
million or more on the economy or
adversely affect productivity,
competition, jobs, the environment,
public health or safety, or state, tribal or
local governments. This determination
was reported in the 71 FR 4161, January
25, 2006. The expected economic result
from instituting the new forestry CXs in
516 DM 11.9C is efficient reallocation of
resources needed to complete NEPA
review from actions, which do not have
a significant effect to those, which may
have a significant effect.
Comment: Some comments question
the amount of money the BLM charges
for permits and timber.
Response: This question is not
relevant to the proposed revisions in
516 DM 11 regarding CXs for permits.
Market values are a local issue, and
values for resources are set by the BLM
Districts based on local economies.
Comment: Some comments noted that
three of the ‘‘proposed new CXs
11.9(7)–(9) mirror new CXs developed
by the Forest Service.’’ They ‘‘by
reference’’ reiterate their concerns about
these FS-based Forestry activities
published in the 68 FR 1026, January 8,
2003, in their comments on the BLM
proposal to adopt CXs 11.9(7)–(9).
Response: The concerns expressed in
the comment are addressed in this
notice of final action where relevant,
and in the case of other concerns, the
relevant FS responses to comments
received and published in 68 FR 44598–
44608, July 29, 2003, are by reference
included in this notice of final action.
The FS Federal Register notice may be
obtained electronically at https://
www.fs.fed.us/emc/lth/notice.pdf.
C(6)—Comments.
Comment: Some comments ask the
BLM to provide a ‘‘sufficient
explanation’’ for why the proposed
Sample Tree Felling (STF) CX 11.9C(6)
is limited to certain areas within
Oregon. Some comments suggest that
the STF CX 11.9C(6) be expanded to all
of Oregon, other Western States, or
BLM-wide.
Response: While the STF survey
method has been used elsewhere, the
BLM reviewed NEPA analysis
specifically to consider the
environmental effects of the STF timber
volume survey method within the
western Oregon lands managed under
the Oregon and California Lands Act
(Pub. L. 75–405, August 28, 1937, as
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amended by Pub. L. 426, June 24, 1954).
The BLM’s Lakeview District, Klamath
Falls Resource Area has been added to
the BLM management units that are
eligible to use CX 11.9C(6), since it is
part of the Oregon and California Lands
Act area where the NEPA analysis and
implementation and effects data are
available. Omission of the Klamath Falls
Resource Area in CX 11.9C(6) was
unintentional. Therefore, Lakeview
District, Klamath Falls Resource Area is
added to the CX as finalized for these
areas. The Prineville District is not
located within the Oregon and
California Lands Act area reviewed, and
has not been included in the CX.
Comment: Some comments state that
the STF CX 11.9C(6) violates the
agreement that the BLM made in a
federal court (Umpqua Watersheds, et
al., v. BLM, No. 00–1750–BR, U.S.D.C.
Or., Stipulation for Dismissal and Order,
13 January 2003). These comments
point out that the new CX will eliminate
a court settlement requiring the BLM to
restrict STF to trees under 20″ dbh.
Response: The CX 11.9C(6) was
proposed to address the terms of the
agreement which states that: ‘‘Unless or
until there is legislative, regulatory, or
other authority adopting a NEPA
procedure for sample tree felling or
exempting such actions from NEPA
procedures, sample tree felling for
timber sale cruising will not occur prior
to the BLM issuing any final decision
document on any BLM District in
western Oregon * * * of any trees over
80 years old * * * of any Douglas-fir
trees 20.0 inches diameter at breast
height (dbh) or greater.’’ Thus, rather
than constituting a violation of this
agreement, this change in the NEPA
procedures for STF was specifically
provided for and anticipated in the
stipulated order resulting from the
settlement agreement. CEQ regulations
at 40 CFR 1507.3 and 1508.4 give the
BLM the authority for adopting a NEPA
procedure to categorically exclude
proposed actions, and based on the
analysis referred to in previous
responses and the analysis available at
https://www.blm.gov/planning/
handouts/CX_ReportSample_Tree_Falling.pdf, the BLM
determined that a CX was appropriate
for STF. CEQ’s testimony before the
House Committee on Resources Task
Force on Updating the NEPA Lessons
Learned Oversight Hearing on
November 17, 2005, reemphasized the
responsibility of federal agencies to
establish appropriate new CXs to
promote efficient NEPA compliance.
Comment: Some comments state that
the proposed STF activities in CX
11.9C(6) could have significant impacts
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on the environment. Other comments
state that the STF CX 11.9C(6) analysis
report (https://www.doi.gov/oepc/
cx_analysis.html or https://
www.blm.gov/planning/news.html) is
flawed because none of the NEPA
processing documents specifically
identified STF as the proposed action
category that could be tied to a finding
of no individually or cumulatively
significant impacts.
Response: Based on the comment
received, the BLM revisited the 2001
through 2005 timber sale EA data used
for the proposed STF CX, which came
from five BLM Districts in western
Oregon (Coos Bay, Eugene, Medford,
Roseburg, and Salem) that have
historically used STF extensively. In the
timber sale EAs analyzed, four of the
five Districts’ data (Coos Bay, Eugene,
Medford, and Salem) did not
specifically address the impacts of STF.
The Roseburg District EAs did
specifically address cumulative effects
of STF as the proposed action category
in their 14 project EAs between October
1, 2001, and September 30, 2005. Based
on the comments received, the BLM
conducted a further review of six
District-wide programmatic STF EAs
(Coos Bay, Eugene, Medford, Roseburg,
Salem, and Lakeview District—Klamath
Falls Resource Area) completed prior to
the 2003 Court Stipulation for Dismissal
and Order (Umpqua Watersheds, et al.,
v. BLM, No. 00–1750–BR, U.S.D.C. Or.,
Stipulation for Dismissal and Order, 13
January 2003). The six District-wide
programmatic EAs were written
specifically to analyze STF in the six
western Oregon districts. Each
programmatic EA analyzed STF effects,
and none were found to be significant.
Analysis from both data sets support the
conclusion that performing STF
activities will cause no individually or
cumulatively significant impacts on the
human environment when the STF
activities are as described in CX
11.9C(6) and when no ‘‘extraordinary
circumstances’’ (516 DM 2.3A(3) and
appendix 2) apply. In all cases where
STF was implemented on the ground,
the actual impacts of STF were the same
as the predicted impacts, and caused no
individual or cumulative significant
impacts.
Comment: Some comments state that
STF is a connected action not subject to
categorical exclusion. They posit that a
proposed STF action is ‘‘always
connected to a commercial timber sale’’
so categorically excluding an STF is a
‘‘segmenting action’’ which could
prevent appropriate consideration of
cumulative impacts.
Response: The BLM position is that
STF and timber sales are not connected
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actions under the NEPA. There are
numerous administrative and
information gathering activities that
occur on forested BLM lands that may
or may not be within proposed timber
sale areas. Many of these activities, e.g.,
stand exams, prescription inventory
plots, wildlife surveys, property line
and boundary surveys, are typically
performed through a basic data
collection CX. These activities are
separate actions that are carried out in
different time periods to provide the
BLM with information to expand the
knowledge of resource values.
Collecting inventory data through stand
exams, conducting wildlife surveys, or
felling sample trees to ascertain volumes
is not directly connected to proposed
actions, and does not make a resource
use allocation decision. If a subsequent
timber sale project is proposed, the BLM
is mandated by regulation (40 CFR 1507
and 1508.4) and the DOI (516 DM 2) to
determine the scope of the proposed
timber sale, consider alternative actions,
and assess the affected environment
through an EA or EIS, as warranted,
including potential cumulative impacts.
Comment: Some comments state that
the proposed STF CX 11.9C(6) violates
a NEPA requirement that actions not be
taken to implement a decision before a
decision is made (e.g., cutting down
sample trees in units that are or could
potentially be allocated in a LUP for a
timber sale). They state that the BLM is
committing resources prejudicing the
ultimate decision.
Response: The BLM disagrees.
Sampling the potential timber yield of
an area to obtain basic resource
inventory data is not equivalent to
making a decision regarding resource
use allocation. There are instances
where for various reasons proposed
timber units or sales have not been
offered, even though sample trees were
cut to gather information on stand
harvest potential. Cutting individual
sample trees at an average density of
less than one tree per acre does not
constitute an irrevocable commitment to
sell the timber stand measured by this
method.
Comment: Some comments state the
BLM should use the NWFP standards
for exempting thinning projects in
stands less than 80 years old from
Regional Ecosystem Office (REO)
review. They state that this action
would help prevent the BLM ‘‘abuse of
discretion in thinning in young stands
to restore old-growth conditions in Late
Successional Reserves (LSR).’’ The
comments suggest that the REO
exemption criteria are based on credible
science that will help to build public
trust/support.
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Response: No changes to the NWFP
are proposed with this CX, and the BLM
will continue to follow the standards of
the NWFP when implementing the CX.
The BLM will continue to follow the
guidance contained in the REO
Memorandum of April 20, 1995,
‘‘Criteria to Exempt Specific
Silvicultural Activities in LSRs and
MLSAs from REO Review.’’ By
following the NWFP standards and the
REO guidance when using the CX, the
BLM concludes that no additional
constraints need be applied, no ‘‘abuse
in discretion in thinning’’ will occur,
and no significant impacts will result.
Comment: Some comments state that
the number of trees to be sampled on
average per acre is too small while
others state the sample size is too large.
Response: The numbers of trees
sampled is not a randomly chosen
number that is easily or arbitrarily
increased or decreased. The numbers of
trees to be sampled are determined by
a statistical equation (refer to the current
the BLM Timber Cruising Handbook, H–
5310–1) and reflect past and projected
future BLM practices. The total number
of sample trees required is less than one
tree per acre on average as shown by the
data and ongoing BLM forestry
management activities.
Comment: Some comments state that
using data from small tree STF to
conclude that there are no impacts to
old-growth STF is not logical. In
addition, these data fail to reveal the
real and cumulative environmental
impacts of cutting old-growth STF. A
related comment made is that if the tree
is older it will be larger, and therefore,
more likely to be included in the STF
sample.
Response: Based on the comments
received, the BLM conducted a further
review, which included six pre-2001
District-wide programmatic EAs for STF
in Coos Bay, Eugene, Medford,
Roseburg, Salem, and Lakeview District,
Klamath Falls Resource Area. These EAs
analyzed the effects of STF on trees of
all ages, including older stands with
timber greater than 80 years of age. Even
with a greater number of large trees
sampled, the environmental impacts are
not significant. Based on the additional
review of the STF Programmatic EAs
and the findings published in the 71 FR
4159–4167, January 25, 2006, the BLM
concludes that when there are no
‘‘extraordinary circumstances’’ (516 DM
2.3A(3) and appendix 2), the 11.9C(6)
CX will not cause individually or
cumulatively significant impacts,
regardless of the age of the stand. The
comment that a larger tree may be more
likely to be included in the sample is
not relevant to the use of a CX, since it
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does not change the conclusion that the
sample size would average less than one
tree per acre, and there would be no
significant impacts from this level of
action.
Comment: Some comments state the
BLM should correct the date on the ‘‘CX
Project—Sample Tree Felling’’ analysis
report (dated January 3, 2005), when the
actual date was January 3, 2006.
Response: The typographic error in
the date of the analysis report has been
corrected. The STF data analyzed were
compiled in November 2005. The NEPA
review process findings discussed in the
analysis report came from STF projects
performed between October 1, 2001, and
September 30, 2005. The BLM
subsequently examined pre-2001
programmatic EAs which resulted in the
same finding—no individually or
cumulatively significant effects
occurred as a result of STF activities
(see last comment and response).
Comment: Some comments state that
the ‘‘CX Project—Sample Tree Felling’’
analysis report should have documented
the high costs associated with
preparation of EAs.
Response: The requested cost-benefit
analysis is not required for this CX.
Comment: Some comments state that
STF sampling should be limited to
young timber stands.
Response: The BLM disagrees. The
STF is used to obtain volume estimates
based on generally accepted survey
methods regardless of the age of the
stand, which requires cutting
representative trees, whether young or
old. STF has been determined to be a
more accurate method of determining
tree volume in large trees because it is
superior to other methods in detecting
defect and measuring tree taper.
Comment: The number of data
analysis ‘‘flaws’’ is a concern. For
example, failure to consider impacts on
old-growth and reserve land allocations,
flawed data collection methods, and
analyzing STF data for only young trees
to justify STF in old-growth forests. The
BLM’s assumptions and conclusion that
STF does not constitute a significant
action as defined by NEPA, could be
wrong.
Response: Based on the comments
received, the BLM revisited the data
used to prepare the ‘‘CX Report—
Sample Tree Felling’’ posted at https://
www.doi.gov/oepc/cx_analysis.html and
https://www.blm.gov/planning/
news.html. The BLM then conducted a
further review of six pre-2001 Districtwide programmatic EAs for STF (Coos
Bay, Eugene, Medford, Roseburg, Salem,
and Lakeview District, Klamath Falls
Resource Area). These EAs included an
analysis of the effects of STF on trees of
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all ages. The data analyzed by the BLM
supports the conclusion that performing
STF activities as described in the CX
11.9C(6), regardless of the timber age,
and when there are no ‘‘extraordinary
circumstances’’ (516 DM 2.3A(3) and
appendix 2), will cause no individually
or cumulatively significant impacts on
the human environment.
Comment: Some comments state that
hundreds of old-growth trees will be
removed if the STF CX 11.9C(6) is
instituted.
Response: By its own terms, the STF
CX 11.9C(6) limits felling, bucking, and
scaling sample trees to an average of one
tree per acre or fewer. The CX does not
include yarding and removal
(harvesting) of trees; therefore,
generally, the trees felled will remain in
situ.
Comment: Some comments state the
BLM should clarify the language used in
CX 11.9C(6). There was concern about:
(a) Interpretation of the qualifier
‘‘approximately one [tree] per acre;’’ (b)
the purpose of the reference to ‘‘use of
ground-based equipment;’’ (c) whether
‘‘temporary’’ roads are considered roads
in this context; and (d) what is meant by
the timber yarding text. Some comments
state that the CX language seems to ‘‘be
a bit open-ended.’’
Response: The CX language for
11.9C(6) has been revised to clarify that
the allowable action or activity is ‘‘less
than one tree per acre on average’’ and
the only tools permitted are ‘‘gaspowered chainsaws and handtools.’’
Road and trail construction (of any type)
and ‘‘timber yarding’’ are expressly
prohibited. The modifications tighten
the language.
C(7)—Comments
Comment: Some comments state that
the 70-acre size threshold is excessively
large for a ‘‘small’’ timber sale. They
state that a 10-acre limit would be more
appropriate based on ‘‘interim policy’’
issued in the 52 FR 30935, August 10,
1987, and reissued in the 53 FR 29505,
August 5, 1988, and again revised in the
57 FR 43180, September 18, 1992.
Response: The BLM disagrees. The FS
updated its ‘‘interim policies’’ to set the
70-acre limit based on a relatively recent
analysis of relevant data (68 FR 44598—
44608, July 29, 2003). The BLM
reviewed the FS changes in acreages
over the 15-year period from 1987 to
2003, which resulted in a different
position from past interim policies, and
concluded that the data supported a FS
size limit change from 10 acres in 1987
to 70 acres in 2003. The BLM
determined that the 70-acre limit is
appropriate to meet the BLM’s needs,
based on its review and comparability
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analysis of the FS data, which was
found to have no individually or
cumulatively significant environmental
effects. Using a 70-acre limit for both the
BLM and the FS will help maintain
consistency between the agencies when
applying CXs. The BLM concluded from
this review that there would be no
significant effect, individually or
cumulatively, from the 70-acre size limit
for these actions on public lands.
Comment: Some comments support
the ‘‘even-aged regeneration’’ limitation,
while others ask that it be stricken from
the 70-acre live tree harvest CX 11.9C(7)
language.
Response: The BLM is not changing
the even-aged regeneration harvest
limitation. Even-aged regeneration
harvests involve a different scope of
environmental effects, which exceed the
supporting data for the live tree
harvesting CX. Uneven-aged harvest
systems (individual tree selection and
group selection) maintain the canopy of
a forest stand; and therefore, have
relatively little effect on the structural
and aesthetic properties of stands. Evenaged regeneration harvests, such as
clearcutting, seed tree, and
shelterwoods, were excluded from use
in CX 11.9C(7). The limitation was
derived from the FS data that showed
the action described in the CX to have
no individually or cumulatively
significant environmental effects, and
which the BLM review and analysis
concluded would cause no significant
effects on the BLM lands. In addition,
the BLM will apply the ‘‘extraordinary
circumstances’’ test to individual
actions covered by the CXs.
Comment: Some comments ask the
BLM to be more ‘‘inclusive of a greater
range of possible live-tree cutting
activities, whether to accomplish fuel
reduction, forest health, wildlife, precommercial thinning, or commercial
timber sale objectives.’’
Response: The CX 11.9C(7) language
includes several examples of when it
may be employed correctly; however,
this is not an exhaustive list of
potentially suitable applications. The
live tree harvest CX focuses on small
timber harvests of 70 acres or less
regardless of the reasons for the harvest
and specifically states the examples
‘‘may include’’ and ‘‘but are not limited
to’’ those examples given in the CX.
Therefore, the activities listed above
could be covered by this CX if they meet
all the CX qualifying criteria and none
of the ‘‘extraordinary circumstances’’ as
defined in 516 DM 2.3A(3) and
appendix 2, apply.
C(8)—Comments.
Comment: Some comments ask the
BLM to define ‘‘dying tree’’ because
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‘‘most mature trees are in some state of
decadence.’’
Response: In the context of proposed
CX 11.9C(8), a dying tree is a standing
tree that has been severely damaged by
forces such as fire, wind, ice, insects, or
disease, and that in the judgment of an
experienced forest professional or
someone technically trained for the
work, is likely to die within a few years.
Comment: Some comments reference
scientific findings that salvage tree
harvesting will increase soil erosion and
sedimentation through multiple
mechanisms. Other comments ask the
BLM to consider the scientific evidence
that salvage tree harvesting is harmful to
the environment and increases wildfire
risk.
Response: The BLM reviewed the FS
data and practices, and determined that
none of the sampled FS projects
resulted in individually or cumulatively
significant environmental effects. This
indicates that agency practices and
guidelines are effective at mitigating
environmental impacts, including soil
erosion, sedimentation, and fire risk.
The BLM’s salvage tree harvesting
practices, guidelines and project effects
are similar to the FS (https://
www.blm.gov/planning/handouts/
CX_Report-Forestry-FS_CXs.pdf).
Therefore, the BLM concludes that by
implementing similar salvage tree
harvesting practices and guidelines, the
BLM’s salvage tree harvesting projects
that use CX 11.9C(8), will have no
significant impacts on environmental
conditions including soil erosion,
sedimentation, or increased fire risk. If
one or more of the extraordinary
circumstances listed in 516 DM 2,
appendix 2 apply, the Responsible
Official cannot use the new forestry
CXs.
Comment: Some comments posit that
there is sufficient scientific evidence
available that contradicts the ‘‘finding
that no significant impacts’’ occur when
the salvage tree harvesting CX 11.9C(8)
criteria are used. They reference several
scientific publications that support a
conclusion that salvage tree harvesting
is damaging to the human environment.
Response: The BLM concludes that
salvage tree harvesting will not have
significant effects on the environment
based on the review of the FS data
where none of the FS sampled projects
showed significant environmental
impacts. As some scientific publications
point out, salvage activities can have
negative environmental impacts,
depending on the condition of the site,
the harvesting system, time of the year,
and other factors. However, both the FS
and the BLM practices and guidelines
have been developed with regard to soil
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and water protection on appropriate
sites that will lead to no significant
effects. This indicates that agency
practices and guidelines are effective at
mitigating environmental impacts,
including soil erosion, sedimentation,
and fire risk. When designing salvage
projects, the BLM uses an extensive
array of guidelines and procedures to
prevent and mitigate negative
environmental impacts during these
activities. The BLM’s salvage tree
harvesting practices and guidelines are
similar to the FS (https://www.blm.gov/
planning/handouts/CX_Report-ForestryFS_CXs.pdf). Therefore, the BLM
concludes that by implementing salvage
tree harvesting practices and guidelines
similar to those implemented by the FS;
the BLM’s salvage tree harvesting
projects that use CX 11.9C(8), will have
no significant impacts on environmental
conditions including soil erosion,
sedimentation, or increased fire risk.
The Responsible Official must consider
the ‘‘extraordinary circumstances’’ (516
DM 2.3A(3) and appendix 2) before
deciding if a proposed action qualifies
for using the CX. If one or more of the
‘‘extraordinary circumstances’’ listed in
516 DM 2 appendix 2 apply, the
Responsible Official cannot use the new
forestry CXs.
Comment: Some comments ask the
BLM to provide the scientific
information necessary to justify an
implied assumption that salvage tree
harvesting has less environmental
impacts than other types of tree
harvesting.
Response: Implied assumptions have
not been used, nor has the BLM stated
whether salvage tree harvesting has
more or less environmental impacts
than other types of tree harvesting. The
purpose of the CX is not to compare the
environmental effects of different types
of tree harvesting, but to determine
whether a CX for salvage tree harvesting
is appropriate. The salvage tree
harvesting CX 11.9C(8) is proposed
based on the BLM’s review of the FS
conclusion that implementing the CX
criteria will ensure that no individually
or cumulatively significant impacts on
the human environment will occur (68
FR 44598–44608, July 29, 2003). Where
significant effects may occur, the FS
concluded that their consideration of
the FS ‘‘extraordinary circumstances’’
(FSH 1909.15, Ch. 30, Sec. 30.3, para. 2)
would not allow the use of the CX. The
BLM has completed a comparison and
finds the FS CX to easily compare with
the BLM CX; and therefore, will
consider using this CX only when the
CX qualifiers apply in full and when
none of the DOI ‘‘extraordinary
circumstances’’ apply (516 DM 2.3A(3)
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and appendix 2). The harvest activity
acreage limits were established by the
FS based on review and analysis of the
data used to establish the CXs (https://
www.fs.fed.us/emc/lth/
1998_details.pdf). The BLM concurs
with the conclusions drawn by the FS,
based on similar management practices
and resulting environmental effects. The
BLM concludes that with the acreage
limitation and other criteria in place,
the actions covered under the salvage
tree harvesting CX will have no
significant effect on the environment,
individually or cumulatively.
Comment: Some comments state that
salvage tree harvesting harms species
protected by the ESA, that the CX fails
to acknowledge that large snags provide
valuable habitat and contribute little to
fire hazard, or that salvage tree
harvesting has significant impacts on
woodpeckers.
Response: The BLM must ensure that
any action authorized, funded, or
carried out by its Responsible Officials
is not likely to jeopardize the continued
existence of any endangered,
threatened, or proposed species (such as
the woodpecker mentioned in the
comment above), or result in the
destruction or adverse modification of
designated critical habitat. The BLM is
required to comply with Section 7 of the
Endangered Species Act, regardless of
the type of NEPA document completed.
The Responsible Official cannot use the
salvage tree harvesting CX 11.9C(8) if
any of the ‘‘extraordinary
circumstances’’ in 516 DM 2.3A(3) and
appendix 2 apply. Extraordinary
circumstance 2.8 (516 DM 2 appendix 2)
specifically prohibits the application of
a CX review process if there is the
potential to have a significant impact on
listed species or their critical habitat.
Comment: Some comments ask the
BLM not to salvage log and gave the
following reasons: Some forested areas
are designated as ‘‘Late Successional
Reserves’’ or ‘‘Critical Habitat Units’’
where the management goals are
incompatible with salvage tree
harvesting; salvage tree harvesting
eliminates important stand history data,
structure, variability, and complexity;
large, decay resistant snags and logs are
important ecologically; and the large
pulse of dead wood created by
disturbance (such as fire and disease) is
significant for an ecosystem’s recovery
over the long-term.
Response: Management goals in LSRs
and salvage tree harvesting are
compatible. For example, the 1994
NWFP and the six 1995 Western Oregon
RMPs provide guidance for management
of federal forest lands in western
Oregon. The NWFP ROD identified
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specific conditions in which salvage
tree harvesting could take place without
negatively affecting the attainment of
LSR goals (NWFP ROD, Standards and
Guidelines for Management of Habitat
for Late Successional and Old-Growth
Forest Related Species Within the Range
of the Northern Spotted Owl, Guidelines
for Salvage pp. C13–C16). Salvage
activities can have negative
environmental impacts, depending on
the condition of the site, the harvesting
system, time of the year, and many other
factors. However, both the FS and the
BLM practices and guidelines have been
developed with regard to soil and water
protection on appropriate sites that will
lead to no significant effects. For
example, in the area covered by the
NWFP, the ROD identified specific
conditions in which salvage tree
harvesting could take place without
negatively affecting Late Successional
habitat goals. All actions must conform
to the LUP management guidelines
regardless of the level of NEPA analysis
completed (43 CFR 1610.5–3).
Comment: Some comments state,
‘‘salvage tree harvesting is not
compatible with contemporary
ecosystem-based management.’’
Response: Salvage tree harvesting is
one of many methods used to achieve a
goal on the landscape, and is compatible
with ecosystem-based management. The
BLM uses ecosystem management to
look at the big picture, beyond federal
agency boundaries, and to work closely
with other land managers, both public
and private. When analyzing effects, the
BLM addresses the long-term
consequences of today’s decisions,
analyzing effects to various resources as
interrelating parts of systems rather than
as individual components to be
managed separately. When
implementing decisions, the BLM uses
many tools. Salvage tree harvesting is
one of the tools used to achieve on-theground goals.
Comment: Some comments state that
there is an increased risk that a
‘‘commercial’’ salvage tree harvesting
project will ‘‘escape’’ sufficient
environmental analysis to prevent
significant environmental impacts.
Response: The BLM disagrees. The FS
data were reviewed for this activity, and
demonstrate that no individually and
cumulatively significant environmental
impacts are likely to occur if the salvage
tree harvesting CX criteria apply and if
a determination is made that none of the
‘‘extraordinary circumstances’’ (516 DM
2.3A(3) and appendix 2) apply. The
BLM determined that establishing the
CX is appropriate. The analytical
findings did not differentiate between
commercial and non-commercial
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activities. The effects on the ground of
a project would be the same regardless
of whether someone is likely to profit
from the venture.
Comment: Some comments state that
there are increased fire risks associated
with salvage tree harvesting which will
be overlooked in the CX review process.
Response: Based on the BLM review
and analysis of the data, the BLM
concludes that actions qualifying for the
CX will not cause a significant increase
in fire risk or fire hazard.
Comment: Some comments ask the
BLM to consider the effects of salvage
tree harvesting by preparing a ‘‘new
programmatic EIS for young complex
forests’’ because the FS and the BLM
‘‘have [not] fully disclosed and
considered current scientific
understandings about the role of fire in
forest development.’’
Response: The role of fire in forest
development is beyond the scope of the
proposed action.
C(9)—Comments.
Comment: Some comments state that
the phrase ‘‘and adjacent live
uninfested/infected trees as determined
necessary’’ should either be eliminated
or quantified to show that a state
licensed, responsible FS or BLM
consultant, employee, or expert in the
field, has validated and documented the
need to harvest adjacent trees.
Response: Federal agency specialists
are qualified to make determinations
necessary in order to carry out their
work in support of the federal
government, and are not required to
have state licenses. A forester or trained
person determines if a tree adjacent to
an infected tree should be removed to
reduce the chance of spreading insects
or disease to the rest of the timber stand.
Typically trees are harvested that are
expected to die within a year and have
indicators such as: No new growth, lack
of leaves during the growing season,
yellowing needles, loss of needles or
leaves in the tree crown, or are
immediately adjacent to dead trees
recently killed by root rot. Sanitation
tree harvesting would not remove all
defective trees as many are left for
wildlife and other resource values.
Comment: Some comments state that
the BLM overestimates the negative
effects of insects and disease and fails
to consider beneficial effects.
Response: The BLM agrees that there
are both negative and positive effects
from insect-infested and diseased trees.
However, the BLM is not placing value
judgments on the positive or negative
effects, but is premising this CX on its
judgment that a FS analysis effort
correctly found that the effects of
sanitation harvesting up to 250 acres
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when specific criteria are met will have
no significant effect, individually or
cumulatively. The harvest activity
acreage limits were determined by the
FS based on review and analysis of the
data used to establish the CXs (https://
www.fs.fed.us/emc/lth/
1998_details.pdf). The BLM concurs
with the conclusions drawn by the FS
and concludes that for BLM actions, due
to similar management practices in
similar ecosystems, the resulting
environmental effects on public lands
will be not significant, individually or
cumulatively. Further, the BLM will
review each proposed action against the
DOI ‘‘extraordinary circumstances’’ (516
DM 2.3A(3)). If any apply, the CX
cannot be used.
Responses to Specific Comments on
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D. Rangeland Management (sub-part
(10)–(12))
D(10)—Comments.
Comment: Some comments ask the
BLM to explain the relationship
between the proposed vegetation
management CX 11.9D(10) and the
‘‘Draft Vegetation Treatments Using
Herbicides on Bureau of Land
Management Lands in 17 Western States
Programmatic Environmental Impact
Statement; Volumes 1 & 2’’ (DVPEIS).
Some comments are concerned that the
proposed vegetation management CX
will ‘‘be abused’’ to meet a threefold
annual increase in treated acres
proposed in the DVPEIS.
Response: The November 2005
DVPEIS (https://www.blm.gov/weeds/
VegEIS/index.htm) analyzed the
potential effects of one of the BLM’s
vegetation management tools
(application of herbicides). The CX
11.9D(10) is established because the
BLM has reviewed the environmental
effects of site-specific routine vegetation
management activities and determined
that those activities, absent
extraordinary circumstances, do not
have individual or cumulative
significant effects and the activities can
proceed without being analyzed in an
EA or EIS. By its own terms, this CX
does not allow its use with respect to
any proposed chemical herbicide action.
Comment: Some comments state that
the justification for the proposed
vegetation management CX 11.9D(10) is
inadequately substantiated. They point
to the fact that the BLM has based its
justification on data from post-fire
restoration efforts and ‘‘no data specific
to the myriad other vegetative
manipulation projects.’’
Response: Though the purpose of
treating hazardous fuels and applying
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post-fire emergency rehabilitation is
different from ‘‘routine management of
vegetation,’’ the actions and resulting
effects are judged to be the same by
professionals in the BLM. Therefore, the
BLM has determined that it is
appropriate to establish this CX based
on these on-the-ground similarities.
Data on routine vegetation manipulation
activities designed to reduce hazardous
fuels and mitigate post-wildfire
environmental impacts were collected
in September 2002 and analyzed in June
2003 to determine whether two CXs
proposed under the Healthy Forest
Initiative (HFI) (68 FR 33813–33824,
June 5, 2003), were appropriate on DOI
and FS lands. These same types of
routine vegetation manipulation
activities, and their effects on the same
lands and resources analyzed in that
context, would be addressed by the CX
under consideration here. In the HFI
context, information on 30 variables for
2,558 projects representing a range of
conditions across the United States was
analyzed. These data included projectspecific information on the location,
size, vegetation type, NEPA review
processes used, predicted
environmental impacts of proposed
treatments, treatments performed, actual
environmental impacts after treatments,
and whether the associated ROD was
appealed. A total of 3,073 treatments, in
various combinations, were applied to
the 2,558 projects. The vegetation
treatments for reducing hazardous fuels
included burning, mechanical thinning,
application of chemical herbicides and
use of biological agents (such as grazing
goats). Some projects had more than one
treatment applied and multiple tactics
such as seeding, planting, tree felling,
and soil stabilizing erosion control
devices were used. The existing HFI
hazardous fuel reduction and
emergency rehabilitation CXs do not
provide for the application of chemical
herbicides or biological agents.
Therefore, for the purpose of the routine
vegetation management CX considered
here, the BLM has proposed the same
activity limits. Further, the BLM
clarified the final CX language to
specifically identify a limitation that no
biological agents may be considered
under the CX.
Comment: Some comments state that
implementing the new CX 11.9D(10)
will not sufficiently address regional or
seasonal environmental concerns.
Response: Regional and seasonal
project design considerations take place
prior to any environmental analyses
based on the professional judgment and
expertise of BLM specialists. The data
set analyzed did not identify a need for
regional or seasonal limitations. The
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vegetation types in the HFI data are
representative of the range of vegetation
structure and conditions across the
United States (refer to the December 18,
2005, ‘‘CX Project—Vegetation
Management analysis report at https://
www.doi.gov/oepc/cx_analysis.html or
https://www.blm.gov/planning/
news.html for details). None of the
treatments that took place under a CX or
an EA/FONSI resulted in individual or
cumulatively significant effects. Further,
the proposed action is reviewed against
the ‘‘extraordinary circumstances’’ (516
DM 2.3A(3) and appendix 2), and if one
applies, the CX cannot be used.
Comment: Some comments state that
adoption and use of the new vegetation
management CX 11.9D(10) will cause
negative impacts on ecosystems by
opening areas to invasive plants
resulting from cross-country travel at
the wrong place and time.
Response: According to analyzed
data, significant impacts, including
exacerbating the spread of invasive
species and/or disruption of the soil
surface as a result of cross-country
travel, did not occur except for 12 of the
2,558 projects in the sample population.
These 12 projects were evaluated
through the EIS process because
significant effects were anticipated prior
to analysis. Similar projects proposed by
the BLM would not be considered for a
CX due to the likelihood that one or
more of the extraordinary circumstances
would apply. In addition, no
unanticipated project-related treatment
impacts were validated by personal
observation by the field staff associated
with the project, field data collection
through a monitoring program, or
systematic evaluation of information
received. Higher level NEPA analysis
was deemed necessary less than 0.5
percent of the time, and those 12
projects for which significant individual
or cumulative impacts were anticipated
were elevated to the appropriate level of
NEPA review. Based on the factual
evidence framed in the context of the
NEPA, adoption of the proposed
vegetation management CX is justified
because 99.5 percent of the projects
analyzed and completed did not have a
significant effect, individually or
cumulatively. Further, those projects
that could possibly have significant
effects would not pass the
‘‘extraordinary circumstances’’ test and
an EA or EIS would be used instead of
a CX.
Comment: Some comments state that
the BLM should not allow projects in
certain high value wildlife areas such as
sage-grouse habitat and potential
wilderness areas unless the proposed
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vegetation management actions are
analyzed by an EA or EIS.
Response: The Responsible Official
must determine the level of NEPA
review required. The potential effect of
a proposed action on high value wildlife
areas such as sage-grouse will be part of
that determination, which will take
place in addition to a review for
‘‘extraordinary circumstances’’ (516 DM
2.3A(3) and appendix 2). The Vegetation
Management CX, by its own terms,
cannot be considered for use in
designated Wilderness or Wilderness
Study Areas.
Comment: Some comments state that
allowing 4,500 acres of public lands to
be treated by prescribed fire without an
EA is irresponsible.
Response: The HFI data reviewed for
the development of this CX revealed no
unanticipated individually or
cumulatively significant impacts from
prescribed fire as long as the area
treated remains at 4,500 acres or less
and none of the ‘‘extraordinary
circumstances’’ (516 DM 2.3A(3) and
appendix 2) apply.
Comment: Some comments suggested
that road construction should only be
carried out following a detailed
analysis. Other road construction is
discussed below.
Response: The vegetation
management CX does not apply to
vegetation management activities
involving new permanent road
construction. Projects involving new
permanent road construction must be
documented through an EA or an EIS.
Comment: The BLM should exclude
prescribed fire from the proposed
revision because prescribed fire causes
significant environmental impacts and
safety risks, and could be an excuse for
building ‘‘temporary roads.’’
Response: The BLM’s review of the
projects considered in the establishment
of the CX revealed that, in the absence
of ‘‘extraordinary circumstances,’’ no
significant effects result from these
treatment actions when the 11.9D(10)
CX criteria are met. Prescribed fire is an
important vegetation management tool
that can be the least environmentally
damaging vegetation treatment option.
Use of prescribed fire was analyzed in
the projects reviewed and the BLM
concluded that the action, if carried out
consistently with the specific criteria
set, did not result in a significant effect.
In addition, while temporary roads
included in the projects reviewed did
not cause a significant effect, in
response to the comment’s request for
clarification, the BLM has added a
definition of temporary road to be used
with respect to when this CX is
considered for use. As an additional
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measure of protection, and to be
consistent with the HFI CX, the BLM
added a limitation to the CX so that no
new permanent road can be constructed.
Comment: Some comments want the
BLM to define the term ‘‘contiguous’’
both spatially and temporally, ‘‘to
prevent abuse and cumulative impacts
to the area’s flora and fauna.’’
Response: The term ‘‘contiguous’’ has
been eliminated to avoid possible
misinterpretation. Each proposed action
must describe the project and the
impacted area in its entirety. Projects
cannot be segmented for purposes of
using this CX. The impacted area of the
proposed action cannot cumulatively
exceed the spatial limits established in
the CX 11.9D(10): 1,000 acres for
qualifying vegetation management
activities, except for prescribed fire,
which can affect up to 4,500 acres.
Based on the spatial and temporal
parameters of the proposed action, the
Responsible Official must determine if
any of the ‘‘extraordinary
circumstances’’ (516 DM 2.3A(3) and
appendix 2) apply. If there is the
potential for individually or
cumulatively significant impacts on the
area’s flora or fauna, CX 11.9D(10)
cannot be used.
Comment: Some comments ask the
BLM not to spray ‘‘untested chemicals’’
under the proposed revisions to CX
11.9D(10).
Response: The BLM has not proposed
that the application of ‘‘untested
chemicals’’ be subject to approval for
any purpose based on use of a CX. The
proposed routine Vegetation
Management CX specifically excludes
the application of herbicides or
pesticides because the data are not
available by which to analyze whether
such an activity should be included in
the category of actions described in the
CX.
D(11) & (12)—Comments.
Comment: Several comments were
received related to proposed CX
11.9D(12) for authorization of nonrenewable grazing use. Comments
included topics such as expanding the
CX to cover actions to improve land
health; questioning the adequacy of the
data analyzed to support the proposed
CX; and requesting that the BLM give
‘‘close scrutiny’’ to the issuance of nonrenewable grazing permits as proposed
in the CX.
Response: Upon review of the
analysis supporting the proposed CX
11.9D(12), and comments received, the
BLM has decided not to finalize the
proposed CX.
Comment: Some comments suggest
that the proposed grazing permit CXs
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directly contradict the BLM’s rationale
for amendments to grazing regulations
proposed on December 8, 2003, (See
final rule 71 FR 39402, July 12, 2006).
Comments express concern that ‘‘[t]he
combined effect of the proposed
categorical exclusion[s 11.9D(11)&(12)]
and the previously-proposed revisions
to grazing regulations will be to
eliminate all opportunities for up front
public consultation regarding the terms
and conditions of grazing permits. The
only remaining opportunities for public
involvement will be the provisions for
after-the-fact protest and appeal under
43 CFR 4160, and even those
opportunities will be eliminated with
respect to temporary, non-renewable
grazing permits.’’
Response: The grazing permit CX
11.9D(11) does not contradict the
rationale for changing grazing
regulations with respect to consultation,
cooperation, and coordination with the
interested public, nor does it result in
the elimination of all opportunities for
up front public consultation. As
explained in the ROD and in the
preamble to the final rule, the final rule
is intended to achieve an appropriate
balance between efficient management
of public lands, and the need for public
involvement (See 71 FR 39414;
Preamble, id at 39439–39441). The same
goals are behind the new grazing CX.
Moreover, ‘‘interested publics’’ will
continue to have opportunities to
participate (‘‘to the extent practical’’) in
public lands grazing management.
Those opportunities arise, during the
development of LUPs and activity plans,
during the development of reports that
lead to a determination regarding status
of land health, and following the
issuance of proposed and final decisions
(See 71 FR at 39432, 39470, and 39475).
During the development or revision of a
RMP, the BLM may decide what public
lands will (or will not) be available for
livestock grazing, change past LUP
decisions, or develop guidance for
making such decisions. In addition, the
BLM may use the land use planning
process to determine if any allotment
management plans (AMPs) will be put
in place. Either during or after the land
use planning process, the BLM develops
the terms and conditions of permits,
leases, and AMPs, such as the
authorized animal unit months (AUMs)
and seasons of use. In this tier of
decision-making, the BLM incorporates
a variety of elements of rangeland
management into a single document.
For example, public scoping conducted
during the revision of an RMP may
prompt the BLM to coordinate the
timing of land health assessments with
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the duration of permits, leases, and
AMPs within a Field Office so that data
from recent land health assessments
will be available at the time of renewal.
The authorized officer (Responsible
Official), using his or her knowledge
and expertise, will identify the relevant
factors, make findings, and integrate
them into a single proposed decision. At
that point, the interested public has an
opportunity to protest, and thereby
affect the decision before it is finalized.
Public participation is a part of the
BLM’s land use planning process, and
enables Responsible Officials to refine
the details of their analysis before they
finalize grazing decisions. However, a
Responsible Official is in the best
position to compile, and consider in the
first instance, the factors that are
relevant to a grazing allotment in a
proposed decision. Thus, the final rule
and the new grazing CX provide for
public input, where most valuable, in
deciding management direction for
public lands. Comments with respect to
temporary non-renewable grazing
permits are moot in view of the BLM’s
decision to not finalize proposed CX
11.9D(12).
Comment: Some comments ask the
BLM to expand the grazing permit CXs
11.9D(11) and (12) by ‘‘adding a
‘resource health activities’ component’’
addressing ‘‘water developments,
fences, etc.’’
Response: The CX 11.9D(11) covers
grazing permit activities where and
when certain conditions are met,
including achievement of land health
standards, or documentation that the
existing livestock grazing is not a causal
factor if standards are not met.
Expanding the CX to include ‘‘resource
health activities’’ as described by the
comment would exceed the scope of the
administrative actions analyzed to
support the CX 11.9D(11). An analysis
of the effects of implementing these
types of projects would need to occur
before a CX could be developed for
these activities. Proposed CX 11.9D(12)
is not being finalized.
Comment: Some comments state that
the fact that most grazing permit EAs
have resulted in FONSIs is insufficient
evidence to demonstrate that EAs are
unnecessary or the impacts are not
significant.
Response: The BLM disagrees. The
BLM established the CX based upon a
review of past environmental
documents, including EAs and FONSIs.
This review showed that in the
overwhelming majority of cases, permit
issuance did not result in significant
impacts to the human environment,
either individually or cumulatively.
Based on comments received in
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response to the proposal of this CX (71
FR 4159–4167, January 25, 2006), as
well as consultation with CEQ, the BLM
collected and reviewed additional
information regarding past actions and
the effects of those actions. This
additional review is intended to clarify
the information previously presented in
the Analysis Report on the issuance of
grazing permits made available in
conjunction with the January 25, 2006,
proposal (see 71 FR 4159–4167, January
25, 2006, https://www.blm.gov/planning/
news.html). The BLM determined a data
refinement was needed that would
facilitate gathering information on a
random basis regarding permits issued
during the period of 1999 through 2004.
Taking this consideration into account,
the BLM determined that the most valid
and reliable method of review would be
to conduct a stratified random sample of
grazing permits issued, drawn from the
BLM’s national Rangeland
Administration System (RAS) database.
A Supplementary Analysis Report
reflecting this refinement of information
regarding NEPA compliance in the
issuance of grazing permits, conducted
based on information in the RAS
database, in response to comments
received, and in consultation with CEQ,
is available at https://www.blm.gov/
planning/news.html. Rather than the
12,724 records of grazing permits issued
presented in the January 2006 Analysis
Report, there are only 9,226 applicable
records in the RAS database for the
relevant time period, 1999 to 2004.
These total figures are different due to
the differing recordkeeping methods of
the BLM Field Offices on the one hand,
and the national RAS database on the
other. Specifically, the BLM field
offices, when queried for the review
reported in January 2006, had returned
total numbers representing all permits
processed during the relevant time
period. The RAS database includes only
those permits processed and actually
issued. Most importantly, the RAS
database identifies by office and state
each permit issued during that timeperiod. Thus, the RAS database
provides an opportunity to conduct a
state stratified random sample of the
permits issued during the relevant time
period. The BLM determined from
review of the sampling of these 9,226
records that 80 percent of grazing
permits issued were issued based on
environmental assessments (EAs)
resulting in Findings of No Significant
Impact (FONSIs). The BLM determined,
based on monitoring, personal
observation, and/or the professional
judgment of BLM rangeland specialists,
that as predicted by these FONSIs,
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permitted grazing resulted in no
significant effects, either individually or
cumulatively. This methodology for
supporting establishment of CXs is
consistent with CEQ’s proposed
guidance for the establishment of CXs
(See 71 FR 54816, September 19, 2006).
For the remaining 20 percent of the
sample of grazing permits issued,
compliance with the NEPA was
documented in a DNA, which is a BLM
procedure for documenting whether
adequate NEPA analysis has already
taken place for a particular action. The
DNAs documented that additional
review was not required, as adequate
analysis had been presented in
previously completed EISs. The BLM
then surveyed the field offices to review
the EIS analysis to determine first,
whether or not grazing permit issuance
itself had been predicted in the EIS to
result in significant effects and second,
whether or not, in their professional
judgment, significant effects had in fact
occurred as a result of the permitted
grazing. Ninety-four of the 458 permits
in the sample, or approximately 20
percent of the sampled permits, had
been issued under a DNA based on an
EIS. The BLM found that of these
ninety-four permits, for five, significant
effects had been identified within the
EIS, and for another one, significant
effects had been documented (through
the Land Health Assessment process) to
have occurred. Therefore, on a weighted
basis, because these numbers were
based on a state-stratified random
sample from the parent population in
the RAS database, the BLM determined
that no more than 3 percent of total
permits issued would have resulted in
significant impacts, either individually
or cumulatively, on the quality of the
human environment. For the remaining
17 percent of the total permits issued
(which used a DNA based on an existing
EIS), the field offices reported that the
resulting effects were not significant.
Based on this review, the BLM is
confident in its projection, that only a
small percentage (no more than 3
percent) of permits issued would result
in significant effects on the
environment. This small percentage
would be screened out by
‘‘extraordinary circumstance’’ review.
Therefore, based on the review of the
data presented in January 2006, as well
as review of the refined data, the BLM
concludes that in the absence of
‘‘extraordinary circumstances,’’ the
issuance of a grazing permit does not
have a significant effect on the
environment, individually or
cumulatively. Further, the BLM in the
establishment of CX 11.9D(11), has
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instituted a limitation for the use of this
CX. This limitation is that the
Responsible Official must determine
(and document the finding) either that
land health standards are met, or that
any failure to meet standards is not the
result of existing livestock grazing.
Comment: ‘‘The BLM has proposed to
revise its NEPA manual to categorically
exclude most term grazing permits (516
DM 11.9D(11)) and most temporary nonrenewable grazing permits (516 DM
11.9D(12)) from analysis under NEPA.
These proposed categorical exclusions
are unlawful, unjustified, and illadvised.’’
Response: The CEQ regulations
implementing the NEPA authorize the
creation and use of CXs. The CEQ
encourages federal agencies to assess
and act upon opportunities to increase
the NEPA efficiency by creating and
using appropriate CXs (40 CFR
1507.3(b)(2)(ii) and 1508.4: See also
‘‘NEPA Lessons Learned Oversight
Hearing, CEQ’’ testimony before the
House Committee on Resources Task
Force on Updating the NEPA Lessons
Learned, 2005). Based on comments
received, the BLM took two actions: (1)
The BLM dropped the proposed nonrenewable grazing permit CX from
further consideration under this manual
revision; and (2) The BLM refined its
analysis of existing NEPA documents
associated with the issuance of grazing
permits (see above response), which had
been reviewed for the establishment of
the 11.9D(11) and has further limited
the situations in which the CX can be
used.
Comment: Some comments state that
the BLM is attempting to substitute the
NEPA environmental assessment
process with the rangeland health
assessment process, and by extension,
that the BLM is assuming there will be
no significant environmental impacts if
rangeland health assessment standards
and guidelines are met.
Response: While land health
assessments are part of the process of
determining the applicability of the
grazing permit CX 11.9D(11), the BLM is
not substituting land health assessments
for NEPA compliance. The CX was
established based on an initial review of
the NEPA documents, for the processing
of grazing permits, reported by the BLM
state offices in January 2006. As
described above, a further refinement
and review of data on grazing permit
issuance, conducted in October through
December 2006, revealed that, on the
whole, issuance of grazing permits does
not result in significant effects,
individually or cumulatively, on the
quality of the human environment. See
discussion of this data refinement above
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and the BLM conclusion that in the
absence of ‘‘extraordinary
circumstances,’’ the actions covered
under CX 11.9D(11) do not have
significant effects, individually or
cumulatively. Rather, the land health
assessment requirement is an additional
limitation the BLM is incorporating into
the CX 11.9D(11). This is in keeping
with CEQ proposed guidance published
at 71 FR 54816, September 19, 2006,
which emphasizes that CXs must clearly
describe a category of actions, and
should include physical and/or
environmental factors that would
constrain its use. The purpose of a land
health assessment is to determine the
status or condition of the land or grazing
allotment. The rangeland assessment
process is not intended to serve as an
analysis of impacts associated with a
particular management action, although
the condition of the land must be
considered if the management action
potentially involves issuing a grazing
permit using the new grazing permit CX
(43 CFR 4180). The land health
assessment process comes into play as
a limitation on use of the CX because
application of the CX is limited to those
permits where allotments are
determined to be meeting land health
standards, or if not meeting land health
standards, this is due solely to factors
other than existing livestock grazing. If
existing livestock grazing management
or level of use is determined to be a
significant causal factor for failing to
achieve standards, federal regulations
mandate that the BLM take appropriate
action to make significant progress
toward achieving those standards (43
CFR 4180.2(c)). If the land health
assessment finds that standards are
being met, the Responsible Official may
fulfill obligations under the NEPA by
using the grazing permit CX, provided
that, in accord with 40 CFR 1580.4, the
Responsible Official determines and
documents that none of the
‘‘extraordinary circumstances’’
(described in 516 DM 2.3A(3) and
appendix 2) applies.
Comment: Some comments state that
administratively allowing the names on
a permit to change, but ‘‘the terms of the
permit to continue unchanged’’ without
further analysis is ‘‘inconsistent’’ under
NEPA and negates an opportunity to
look at ground conditions.
Response: The BLM deleted part (b) of
CX 11.9D(11) to clarify the intent of the
CX to require completion of a land
health assessment before application of
a CX could be considered. Therefore,
administrative changes such as changes
of names on grazing permits are subject
to CX 11.9D(11) and its criteria
involving the completion of land health
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assessments. ‘‘Ground conditions’’ are
evaluated in the land health assessment
process. Existing monitoring and
inventory data and information gathered
using the BLM approved techniques are
used to evaluate conditions in relation
to the standards developed by the BLM
state directors in consultation with their
respective Resource Advisory Councils
as directed in 43 CFR 4180.2. Changing
the name on a permit does not change
on-the-ground management or the
effects of implementing the other terms
and conditions of the permit. The
modification of CX 11.9D(11) will
assure that land health assessment
findings are considered when making an
‘‘administrative’’ change.
Comment: Some comments state that
the federal courts have determined that
grazing permits significantly affect the
human environment.
Response: In 1974, a federal court
stated that ‘‘[t]he court is * * *
persuaded that the grazing permit
program produces significant impacts
on individual locales. And when the
cumulative impact of the entire program
is considered, it is difficult to
understand how defendants-intervenors
can claim either that the impact of the
program is not significant or that the
Federal action involved is not major.’’
NRDC v Morton, 388 F. Supp. 829, 835
(D.D.C. 1974), aff’d, 527 F.2d 1386 (DC
cir 1976), cert. denied, 427 U.S. 913
(1976). As a result of this ruling, the
BLM agreed to (and did) analyze the
effects of the BLM grazing program in
over 140 local EISs covering
approximately 160 million acres. The
Interior Board of Land Appeals (IBLA)
subsequently held in National Wildlife
Federation v. BLM, 140 IBLA 85 (1997)
that, in the Comb Wash allotment, the
general analysis for the LUP did not
provide adequate site-specific analysis
of the effects of livestock grazing.
Consequently, the BLM issued guidance
in Washington Office Instruction
Memorandum 99–039 Attachment 3
explaining that existing NEPA
documentation should be reviewed to
determine if adequate analysis had
already been completed, and where
existing documents were not adequate,
adequate NEPA documents should be
developed. The BLM Responsible
Officials have instituted these
directives. Based on comments received
in response to the January 2006
proposal to establish new CXs, as
explained above, the BLM refined its
review and analysis of NEPA documents
associated with all grazing permits
issued in 1999 through 2004 (9,226
projects). See the data refinement
discussion above. Approximately 80
percent of the 9,226 grazing permits
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issued from 1999 through 2004 were
based on EA/FONSIs. The remaining 20
percent of permits sampled used a DNA,
which indicated an existing EIS
represented sufficient analysis to
support issuance of the grazing permit.
In addition to the review of the NEPA
documents, BLM specialists used
monitoring, personal observation and/or
professional judgment to evaluate the
permitted grazing. This evaluation of
the NEPA documents and any actual
impacts not anticipated in the NEPA
documents revealed that significant
impacts were estimated to be (weighted,
on the basis of a state-stratified random
sample), at most, 3 percent of the
permits issued between 1999 and 2004,
with a high degree of certainty. The
BLM believes the ‘‘extraordinary
circumstances’’ review would preclude
use of CX 11.9D(11) in similar
circumstances. Establishment and
appropriate use of the grazing permit CX
11.9D(11) is warranted based on the
analysis described above and in the
Supplementary Analysis Report.
Establishment and appropriate use of
the CX is also warranted in the context
of the BLM administrative procedures
such as the BLM Qualifications and
Preference Handbook (H–4110–1), the
state-specific standards and guidelines,
and the specific terms and conditions
identified within local LUPs. The
extraordinary circumstances review
provides additional protections to
prevent the issuance of permits through
a CX when significant individual or
cumulative impacts are likely to occur.
Comment: Some comments state that
the statistics presented in the ‘‘CX
Project—Grazing Permit’’ analysis report
posted at https://www.doi.gov/oepc/
cx_analysis.html and https://
www.blm.gov/planning/news.html are
‘‘extraordinarily misleading’’ because
they fail to reveal the multiple instances
in which the federal courts or DOI
administrative law judges have found
that the BLM violated NEPA by failing
to prepare an EIS. The example cited
was Western Watersheds Project v.
Bennett, 392 F. Supp. 2d 1217 (D. Idaho
2005).
Response: These comments highlight
a case in which the court found that the
BLM had erred in preparing four EAs
associated with four grazing permits for
28 grazing allotments in the Jarbidge
Resource Area in Idaho. The BLM
should instead have prepared a single
NEPA document covering all four
permits. It is speculative to suggest that
this finding undermines the BLM’s
analysis of thousands of permits.
Moreover, a careful reading of the
court’s opinion reveals that none of the
grazing decisions at issue in that case
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would have been eligible for use of the
new CX, because land health
assessments had shown that land health
standards were not being met in any of
the allotments—generally because of
grazing. Further, the BLM believes that
existing NEPA compliance procedures
would have rendered the proposed
actions involved in the Western
Watersheds Project v. Bennett case
ineligible for the new grazing permit CX
11.9D(11) based upon review of the
‘‘extraordinary circumstances.’’
Specifically, ‘‘extraordinary
circumstance’’ 516 DM 2 appendix 2.8
would have applied. This extraordinary
circumstance applies when a proposed
action may have significant impacts on
species listed, or proposed to be listed,
on the List of Endangered or Threatened
Species, or have significant impacts on
designated Critical Habitat for these
species.
Comment: The same comments state
that ‘‘[I]t is likely that many of the EAs
and FONSIs tabulated in [the ‘‘CX
Project—Grazing Permit’’ Analysis
Report] were not subject to challenge by
environmental, conservation, or wildlife
interests. Experience has shown that,
when subject to administrative or
judicial challenge, a high percentage of
the BLM’s FONSIs for grazing permits
are found to be unlawful. If more had
been challenged, it is likely that many
more of the FONSIs would have been
overturned and environmental impact
statements (EISs) would have been
required.’’
Response: These comments are
speculative in nature. An administrative
or judicial challenge to a particular EA
and FONSI may result in a ruling that,
for example, an agency failed to take a
hard look in a particular instance.
However, it is unreasonable to assume
that EAs and FONSIs that were never
protested or appealed were unlawful.
Comment: The same comments ask
the BLM to ‘‘survey the EAs that have
been prepared for grazing permits to
determine the nature and scope of the
information and analysis that they have
contained and the public comment that
they have engendered.’’
Response: The BLM reviewed data
relating to the NEPA documents for
grazing permits that were completed in
1999 through 2004. CX 11.9D(11) has
been established based on the finding
that the overwhelming majority of these
NEPA documents (EAs prepared in
accordance with CEQ regulations and
agency guidance) resulted in FONSIs
and subsequent BLM review of the
actual effects of grazing confirmed this
prediction. For those proposed permits
for which a DNA reflected the prior
completion of adequate NEPA, at most
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(weighted, based on a state-stratified
random sample), only 3 percent were
found to have resulted in a significant
effect, either individually or
cumulatively. The CX would not have
been considered for use with those
actions found to have significant effects,
as one or more of the ‘‘extraordinary
circumstances’’ would have applied.
The BLM concluded, based on this
evidence, that the issuance of grazing
permits is an action that does not have
a significant impact on the human
environment, either individually or
cumulatively. This is in accord with the
CEQ proposed guidance on the
establishment of CXs (See 71 FR 54,816,
September 19, 2006). Use of this CX in
light of an ‘‘extraordinary
circumstances’’ review provides a
further safeguard that significant
impacts will be avoided. The BLM
believes additional analysis of the type
requested is not required.
Comment: Some comments state that
the proposed revisions to the grazing
permit process remove environmental
safeguards by reducing the amount of
information needed.
Response: In order to establish the
grazing permit CX, the BLM reviewed
NEPA analyses completed in the
process of issuing 12,724 permits over a
five-year period and then, as explained
above, further refined this analysis by
sampling 9,226 permits identified in the
RAS database. These permits were
processed regardless of whether or not
land health assessments had been
completed for the relevant allotments.
The results of that review show that
impacts to the human environment from
the issuance of grazing permits are not
significant, either individually or
cumulatively. The CEQ regulations
support the establishment of a CX in
circumstances where the review of data
shows that impacts of a particular action
have not been significant, either
individually or cumulatively. Not only
does the required review of the
‘‘extraordinary circumstances’’ provide
a safeguard when using the CX, but also
the specific criterion that a land health
assessment must have been completed,
and result in a certain finding, provides
an additional safeguard at the outset.
This is in keeping with CEQ proposed
guidance published at 71 FR 54816,
September 19, 2006, which emphasizes
that CXs must clearly describe a
category of actions, and should include
physical and/or environmental factors
that would constrain its use. As part of
the CX criteria, land health assessment
and evaluation information and status
are considered. The evaluations are
based on existing inventory and
monitoring information, data collected
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using BLM-approved methods, and, if
appropriate, information provided by
other sources, such as other agencies,
permittees, or the interested public. The
grazing CX cannot be used unless the
specific CX criteria are met and none of
the ‘‘extraordinary circumstances’’
applies.
Comment: Some comments correctly
assume that rangeland health ‘‘Land
Health’’ assessments only look at a
limited set of environmental concerns
covered by the NEPA. These same
comments express concern that impacts
on certain resources covered by the
NEPA (e.g., archeological sites) are not
specifically evaluated and use of CXs
(11.9D(11)&(12)) will preclude
appropriate consideration of resources
not included in land health
assessments.
Response: Use of the grazing CX
11.9D(11) requires review against the
list of ‘‘extraordinary circumstances.’’
Two of the ‘‘extraordinary
circumstances,’’ 516 DM Ch appendix
2.2 and 2.7, ensure that ‘‘cultural
resources’’ will not be affected by the
proposed action; therefore, impacts to
cultural resources are not overlooked
when a grazing permit is processed
through CX 11.9D(11). In addition, use
of the CX (or any CX) does not eliminate
the need to comply with statutes such
as Section 106 of the National Historical
Preservation Act and the Archeological
Resource Protection Act (1979).
Comment: Some comments question
some of the key terms and concepts in
the grazing permit CXs 11.9D(11)&(12):
(1) ‘‘Assessed and evaluated,’’ (2)
‘‘meeting land health standards,’’ and
(3) ‘‘not meeting standards solely due to
factors other than existing livestock
grazing’’ are arbitrary, and ‘‘ [N]ot
meeting standards solely due to factors
other than existing livestock grazing’’ is
an admission that ‘‘the land is in poor
condition.’’ The comments go on to say,
‘‘[I]f the land is already degraded, the
approval of a lease, absent any NEPA
review, will only further devastate the
land and result in substantial
environmental impacts.’’
Response: In keeping with CEQ
proposed guidance published at 71 FR
54816, September 19, 2006, which
emphasizes that CXs must clearly
describe a category of actions, and
should include physical and/or
environmental factors that would
constrain its use, the land health
standards serve as a screen to ensure
that the grazing CX is considered for use
only where land health standards are
being met or if not being met, the cause
is not existing livestock grazing use. The
concept of ‘‘meeting land health
standards’’ is derived from grazing
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regulations in 43 CFR 4180.2. These
regulations require action to change
existing grazing if the Responsible
Official finds that current livestock
grazing is a significant cause for ‘‘failing
to achieve the standards.’’ The reference
to ‘‘not meeting land health standards
solely due to factors other than existing
livestock grazing’’ follows from the
same regulatory requirement, but is
somewhat more restrictive than the
language in the regulations, in that the
CX may only be used when existing
livestock grazing is not at all a
contributing factor for failure to achieve
standards. Assessments and evaluations
are not arbitrary concepts; they are the
means for determining whether
standards are achieved and identifying
the causal factors for ‘‘failure to
achieve.’’ If standards are not achieved
because of another activity, then that
activity needs to be addressed (BLM
Rangeland Health Standards Manual
4180). For example, during the course of
a land health assessment the BLM could
determine that the amount of dead and
down woody material in an area of
forested lands is causing an unnatural
build-up of fuels and that the resulting
potential for a severe wildfire is an
indication that the land is failing to
meet one or more of the land health
standards. In this example, the interdisciplinary team determines that
livestock grazing is not a contributing
factor to the unnatural build-up of
woody fuels that resulted in nonachievement of the standard. This is one
example of a situation where changes
in, or denial of a grazing permit/lease
would not influence attainment of the
land health standard(s).
Comment: Some comments state that
the BLM’s ‘‘land health standards are
not sufficiently demanding’’ to prevent
significant environmental impacts or to
restore degraded lands. The ‘‘bar for
compliance is pretty low and * * *
most * * * [allotments] routinely pass
* * * regardless of condition.’’
Allotments can ‘‘meet land health
standards’’ and still ‘‘have important
and unresolved resource issues which
are more likely to be ignored in a CX
than an EA.’’
Response: Based on the data analyzed
for establishment of the grazing CX
11.9D(11), as explained above, 80
percent of the NEPA documents
prepared in support of issuing grazing
permits predicted no significant effect
on the quality of the human
environment, and subsequent BLM
review of the actual effects of grazing
confirmed this prediction, regardless of
whether the allotment for which the
permit was issued had undergone a land
health assessment. For the (at most 3
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percent) grazing permits issued, that did
or may have (projecting on the basis of
the sample reviewed) result(ed) in
significant effects, the BLM’s NEPA
review procedures that are in place to
review proposed actions against the
DOI’s ‘‘extraordinary circumstances’’
would have rendered the actions that
did result in a significant effect as
ineligible for CX consideration. The
BLM believes that for issuing grazing
permits in the future, the review of the
‘‘extraordinary circumstances’’ will
identify significant unresolved issues
related to grazing use. When any of the
‘‘extraordinary circumstances’’ apply, a
CX cannot be used even if land health
standards are met. The BLM has placed
a limitation on the use of the CX
11.9D(11), which only allows
consideration of the grazing permit CX
when an allotment is meeting land
health standards or is not meeting land
health standards for reasons other than
livestock grazing. As explained above,
the inclusion of this limitation is in
accord with CEQ proposed guidance
published at 71 FR 54816, September
19, 2006.
Comment: Some comments state that,
‘‘ ‘and health standards’ evaluations are
not conducted often enough and get
outdated quickly when drought, fire,
and other circumstances occur. This is
particularly problematic when a [nonrenewable permit] is to be issued.’’
Response: The grazing permit CX
11.9D(11) cannot be used if land health
standards have not been assessed or
evaluated, and the evaluation team is
responsible for the adequacy of the
information. As discussed above, the
non-renewable grazing CX 11.9D(12) is
not being finalized. No grazing permit
can be issued under CX 11.9D(11)
unless CX criteria are satisfied and none
of the ‘‘extraordinary circumstances’’
(516 DM 2.3A(3) and appendix 2)
applies.
Comment: Some comments state that
the new grazing permit CXs ‘‘would
permit inappropriate grazing * * * to
pollute streams and watersheds * * *. ’’
Response: The CXs, EAs, FONSIs, and
EISs do not ‘‘permit’’ grazing or any
other activity on public lands, they
document fulfillment of procedural
requirements under the NEPA. When
the proposed action consists of a permit,
lease, or other grazing authorization, the
NEPA compliance for these actions
cannot end with a CX unless an
authorized officer (Responsible Official)
has completed a land health assessment
for the relevant allotment, and has
concluded that the 43 CFR 4180
standards for grazing administration are
being achieved. Since all state and
regional standards address water quality
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and other ecological criteria, the BLM is
confident that the use of CXs will not
result in the pollution of streams and
watersheds.
Comment: Some comments say that
rangeland health ‘‘land health’’
assessments do not address the
cumulative impacts of grazing on
multiple allotments.
Response: The land health
assessments are not meant to replace the
NEPA analysis and do not directly
address cumulative impacts. As
explained above, in accordance with
CEQ proposed guidance (71 FR 54816,
September 19, 2006), which
recommends that categorical exclusions
should clearly define a category of
actions, as well as any physical or
environmental factors that would
constrain its use, the BLM has
incorporated this limitation as criteria
for the use of the CX in relation to
issuance of a grazing permit. The land
health assessment would serve as a
‘‘screen’’ to determine if a CX might be
considered for issuing a grazing permit.
The land health assessment process
identifies whether or not the land health
standards are being achieved, and if
they are not achieved, the causal factors
are identified. Therefore, they do
provide useful information about
whether grazing is contributing to nonachievement of one or more of those
standards. Cumulative impacts of
grazing on multiple allotments are often
analyzed at the LUP allocation level
under an EIS or EA, but that analysis
may also occur within a more program
specific NEPA document. Individual
grazing permits can be issued within the
scope of such LUP NEPA analysis and/
or appropriate program specific NEPA
analysis. Issuance of the grazing permit
would be based on the resource
allocation of the LUP or other programspecific plan. Any additional mitigation
measures or other restrictions in grazing
use, prescribed in the NEPA analysis
that addressed cumulative impacts
associated with grazing, would be
incorporated in the grazing permits
issued within the scope of that NEPA
analysis. As explained above, based on
the data analyzed for establishment of
the grazing CX 11.9D(11), 80 percent of
the NEPA documents associated with
issuing grazing permits resulted in a
FONSI. That is, the evidence showed
that the action of issuing grazing
permits was predicted not to result in
significant impact to the human
environment, either individually or
cumulatively and BLM specialists
through monitoring, personal
observation and/or professional
judgment confirmed these predictions.
As an added safeguard, when
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considering issuance of individual
grazing permits, the Responsible Official
must consider the DOI ‘‘extraordinary
circumstances.’’ If ‘‘extraordinary
circumstance’’ 516 DM 2.3A(3) and
appendix 2.6, regarding significant
cumulative impacts applies, the grazing
CX cannot be used, and an EA or EIS
would be prepared.
Comment: Some comments viewed
the revisions as enabling ‘‘unsustainable
grazing permits.’’
Response: It is unclear what is meant
by ‘‘unsustainable grazing permits.’’ In
the context of the Federal Land Policy
and Management Act, 43 U.S.C. 1701 et
seq. (FLPMA), the BLM is required to
administer public lands for multiple use
and sustained yield. The BLM grazing
permits are managed in accordance with
FLPMA, the Taylor Grazing Act, 43
U.S.C. 315 et seq., and the Public
Rangelands Improvement Act, 43 U.S.C.
1901 et seq. An element of this
management is a requirement to
authorize grazing permits that do not
preclude achievement of land health
standards, consistent with these
statutory mandates. The grazing CX
11.9D(11) is being established based on
evidence that grazing decisions do not
result in significant impacts to the
environment, either individually or
cumulatively. The BLM data show that
the predictions represented by the EAs
that resulted in FONSIs were confirmed
by BLM professionals through
monitoring, personal observation and/or
professional judgment. The grazing CX
11.9D(11) can be used only for those
permits being issued for livestock
grazing on allotments where land health
standards are achieved under existing
grazing management, or where a
Responsible Official finds that standards
are not achieved due to factors that do
not include existing livestock grazing. If
standards are not met and current
livestock management is one of several
activities contributing to the nonachievement of the standards, a grazing
permit cannot be issued using the new
grazing permit CX, and an EA or EIS
must be prepared unless the permit is
withdrawn. Further, any use of a grazing
CX would require review against the
‘‘extraordinary circumstances,’’ and if
one applies, a CX cannot be used, and
an EA or EIS would be prepared.
Comment: Some comments state that
the analysis methods were not
sufficiently disclosed which means the
data set and the data interpretation
could be flawed.
Response: As stated in the analysis
report, available at https://www.blm.gov/
planning/news.html, the data analyzed
included a review of 12,724 NEPA
documents associated with grazing
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permits issued between October 1, 1999,
and September 30, 2004. Based on this
comment, as well as consultations with
CEQ, the BLM further refined its
analysis, reviewing data from the RAS
database, the official source of grazing
administration data for the BLM, instead
of from individual state reports, as were
used in the January 2006 analysis
report. Use of the information in the
RAS database provided the BLM with
an appropriate set of data from which to
draw a stratified random sample for
analysis. See the refined analysis report
at https://www.blm.gov/planning/
news.html. This refinement of the data
on grazing permits resulted in 9,226
records, rather than the 12,724
presented in the January 2006 Analysis
Report. This review based on the
information in the RAS database
ensured that only records of permits
actually issued, not just processed, were
being reviewed and eliminated the
possibility of inappropriate inclusion of
those permits issued pursuant to
specific congressional authorization,
regardless of completion of the NEPA
process (see Pub. L. 108–108, Section
325, 117 Stat. 1307–1308 (2003)). The
BLM determined from review of these
9,226 records that 80 percent of grazing
permits issued were issued based on
EAs resulting in FONSIs. Further, the
BLM determined, based on monitoring,
personal observation, and/or
professional judgment by BLM
rangeland specialists, that, as predicted
by these FONSIs, permitted grazing
resulted in no significant effects, either
individually or cumulatively. This
methodology for supporting
establishment of CXs is consistent with
the CEQ’s proposed guidance for the
establishment of CXs (See 71 FR 54,816,
September 19, 2006). For the remaining
20 percent of grazing permits issued, in
the majority of cases, the DNA review
documented that additional NEPA
review was not necessary. The issuance
of the permits had been adequately
analyzed in an existing EIS prepared in
the course of the land use planning
process or specifically prepared to
address grazing issues. The BLM
concludes from this review that, in
general, the issuance of grazing permits
results in no significant impacts and
establishment of a CX is warranted. The
BLM believes that ‘‘extraordinary
circumstances’’ review will capture
those instances for which additional
NEPA review will be necessary, such as
the 3 percent (weighted, on the basis of
a state-stratified random sample
analysis) of permits issued in
conjunction with a DNA prepared on
the basis of an existing EIS, for which
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significant impacts were either
predicted to occur, or though not
predicted, were observed (during the
land health assessment process) to have
occurred. In this regard, the results of
the additional data calls conducted in
October 2006, as reflected in the
Supplemental Analysis Report, are
consistent with the results originally
presented in the Analysis Report
published in January 2006, which
showed that in only a few cases (0.2%)
did issuance of grazing permits/leases
require preparation of a new EIS
because of specific resource reasons.
Comment: Some comments ask
whether any land health assessments
are based on ‘‘observations’’ alone
(ocular estimates). Other comments
express an opinion that ‘‘[o]cular
monitoring to determine the range
condition and trend makes management
[of grazing permit decisions based on
observations alone] arbitrary and
capricious.’’
Response: The BLM does not use
exclusively qualitative (i.e. ‘‘ocular’’ or
‘‘observational’’) methodology to
determine trend. The BLM’s Rangeland
Health Standards Handbook (H–4180–1)
provides guidance on using qualitative
(‘‘observational’’) and quantitative
information to determine the status of
land health. In addition, the BLM’s
Technical Reference, Interpreting
Indicators of Rangeland Health, Version
4 (TR1734–6) describes land health
assessment protocols, developed
through an interagency process, which
have received interdisciplinary review.
TR 1734–6 identifies limitations for
using the results derived from the
qualitative (‘‘ocular’’/‘‘observational’’)
process. For example, TR 1734–6 states
that the qualitative process described in
the document is not suited to detecting
land health condition trends.
Qualitative methods are appropriate for
certain purposes, but quantitative data
are needed to detect and statistically
validate trends. When an assessment is
done, existing monitoring data are
evaluated. This data can be the result of
either quantitative or qualitative
methods. Where these data do not
address all of the standards, the BLM
employs the processes described in TR
1734–6 to assess conditions. Within the
limits described in this TR 1734–6,
qualitative approaches, such as ocular
or observational methods, are important
tools for assessing conditions, but not
trends.
Comment: Some comments ask that
management alternatives that could
improve land health conditions not be
excluded from the new grazing permit
CXs 11.9D(11)–(12). These comments
recommend modifying the new grazing
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permit CXs to allow changes to the
authorized grazing activities that might
improve ground cover, soil stability, and
other conditions to reduce conflicts
with other resource uses.
Response: The BLM’s purpose in
establishing CX 11.9 D(11) is to expedite
the permit issuance process where the
environmental impacts have been
shown not to be significant, either
individually or cumulatively. In
appropriate circumstances, it may be
possible to apply the CX to
modifications (e.g. reduced level of
grazing) that might improve ground
cover, soil stability, and other
conditions to reduce conflicts with
other resources so long as the terms of
the CX are met and the overall effects of
the livestock grazing permit do not
result in an inability to meet land health
standards. Further, a CX may only be
used when none of the ‘‘extraordinary
circumstances’’ applies. If any of the
‘‘extraordinary circumstances’’ applies,
then the proposed action (including the
actions listed in the comment) may
require preparation of an EA or EIS.
Because the proposed CX 11.9D(12) is
not being finalized through this action,
the potential applicability of proposed
CX 11.9D(12) will not be addressed
here.
Comment: Some comments state that
the grazing permit CXs 11.9D(11)–(12)
will ‘‘allow the BLM to issue a permit
for any number or type of livestock, for
any season, [for any given time period],
with (or without) any terms and
conditions, without performing any
analysis pursuant to NEPA.’’
Response: The CEQ regulations
provide that NEPA obligations can be
fulfilled using categorical exclusions (43
CFR 1507.3 and 1508.4). The CX
11.9D(11) has been established based on
review of analyses of NEPA documents
completed in the process of issuing
grazing permits. This review showed
that in the vast majority of cases, this
action of issuing a grazing permit
resulted in a FONSI and that as
described above, only a very small
percentage (3 percent, weighted, as
based on a state-stratified random
sample) resulted in significant effects.
The BLM believes that ‘‘extraordinary
circumstances’’ review would have
precluded use of the CX in the
circumstances represented by this small
percentage of instances. The BLM
concluded based on its review of the
resulting effects of the grazing permit
issuance action that, in the absence of
‘‘extraordinary circumstances,’’ there
are no significant effects, individually or
cumulatively. Use of this CX is
specifically limited in two ways. First,
the permitted use must be basically the
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same as that previously authorized
(same kind of livestock, the active use
is not exceeded, and the grazing season
is not more than 14 days earlier or later
than the use authorized on the previous
permit/lease). Second, the land health
standards must be met or if the
standard(s) are not met, this can only be
due to factors that do not include
existing livestock grazing. If the permit
action is ineligible under these criteria,
then grazing permit CX 11.9D(11)
cannot be used. As mentioned above,
CX 11.9(D)(12) is not being finalized
through this action.
Comment: Some comments identify
‘‘six resources categories’’ that are
adversely affected by livestock grazing
and its associated infrastructure
(facilities), which they state are not
addressed by land health standards. The
six categories they identified are
archeological sites, wilderness, scenery,
recreational opportunities, wildlife
other than listed and ‘‘sensitive’’
species, and natural surface water
sources. They contended that, if the
grazing permit CXs 11.9D(11)–(12) are
adopted, analysis and consideration of
the impacts on these resources would
never occur on any allotment that meets
minimal standards for land health.
Response: Water quality and wildlife
habitat standards are addressed in all
the sets of state or regional land health
standards. Two of the six resources
mentioned in the comment (archeology
and wilderness) are specifically
addressed in the ‘‘extraordinary
circumstances’’ found in 516 DM 2,
appendix 2.2. In addition, appendix 2.2
refers to recreation, wild and scenic
rivers, national natural landmarks, sole
or principle drinking water aquifers,
wetlands, floodplains, migratory birds,
and other ecologically significant or
critical areas. ‘‘Infrastructure’’ that
facilitates management of livestock
grazing is not addressed in the CX. Such
infrastructure (also known as ‘‘range
improvements’’) would be addressed in
AMPs and project proposals and would,
in accordance with 43 CFR 4120.3–1(f),
receive appropriate NEPA review
separate from CX 11.9D(11).
Comment: Some comments state that
rangeland health ‘‘land health’’
assessments fail to address many
significant impacts of grazing.
Response: Land health assessments
are not intended to analyze the impacts
of grazing, but to determine the existing
condition of the public land in
comparison to the land health standard.
If the Responsible Official determines
that land health standards are not being
achieved, a determination is made
regarding the significant causal factor(s).
If the Responsible Official finds that
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current livestock grazing management or
levels of use are significant causal
factors for failure to achieve land health
standards, they are directed by
regulation (43 CFR 4180.2) to take
appropriate action to make significant
progress toward achieving the
standard(s) not achieved. The issue of
whether there are any significant
impacts from the BLM-permitted
grazing is addressed pursuant to
compliance with the NEPA at the time
permits are issued. Use of a CX, like the
grazing CX 11.9D(11) is a method of
complying with the NEPA (see 40 CFR
1500.4(p); 40 CFR 1500.5(k); 40 CFR
1507.3; and 40 CFR 1508.4). As
explained above, the grazing CX
11.9D(11) has been established based on
the results of a review of NEPA
documents associated with the issuance
of grazing permits over a five-year
period and the subsequent BLM review
of the actual effects of grazing confirmed
this prediction. The review shows that
this category of actions (issuing permits)
has no significant impact on the human
environment, either individually or
cumulatively and would not normally
warrant preparation of an EIS or EA.
Land health assessments are not the
only screen for determining whether the
grazing CX 11.9D(11) may be used. The
‘‘extraordinary circumstances’’ also
provide screening for application of the
CX.
Comment: Some comments ask these
questions: ‘‘What is the required time
period and nature of the assessment?’’
‘‘Is it a detailed FRH [Fundamentals of
Rangeland Health] assessment or a
cursory review by a BLM team?’’
Response: An assessment consists of a
review of existing monitoring and
inventory data, and a review of the
status of selected indicators using BLM
TR 1734–6. The assessment may include
a collection of new monitoring data
when there is inadequate information to
make a determination of status or causal
factors for non-achievement. In 1998,
the BLM directed State Offices to
develop a strategy to complete an
assessment of current conditions in
relation to land health standards and to
strive to assess about 10 percent of their
land each year. Washington Office
Instruction Memorandum No. 98–91
provided direction to assess high
priority areas first. The Responsible
Official usually determines the level of
intensity of the assessment based on
issues, availability and currency of
existing inventory and monitoring data,
and amount of information needed to
make a determination of status and, if
necessary, to determine causal factors
where land health standards are not
achieved. The land health assessment
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process is described in the BLM’s
Rangeland Health Standards Handbook
(H–4180–1) available at the BLM’s Web
site https://www.blm.gov/nhp/efoia/wo/
fy01/im2001-079.html.
Comment: Some comments ask the
BLM to include a ‘‘requirement as to the
[currency and] quality of the data
involved’’ to ensure that the BLM is
‘‘employing the Best Available
Science.’’
Response: CEQ regulations at 40 CFR
1502.22 and 1502.24 include
requirements that an EIS include
‘‘credible scientific evidence’’ (1502.22),
and that ‘‘agencies shall ensure the
professional integrity, including
scientific integrity of discussions and
analyses in environmental impact
statements.’’ (1502.24). The BLM
conducts its environmental reviews and
analyses in accordance with guidance
contained in programmatic handbooks
and technical references to ensure the
professional integrity of the information,
discussions, and analyses. For example,
the BLM’s Rangeland Health Standards
Handbook (H–4180–1) provides
direction for collecting and evaluating
information used in determining the
status of land health. The BLM’s
Rangeland Health Standards Handbook
(H–4180–1) contains a lengthy
discussion of the availability and
adequacy of existing data including
factors such as the age, scale, and
appropriateness of the data to be used.
Professional judgment may be used to
draw conclusions where quantitative
data does not lead to definitive
conclusions; but the reasoning behind
the use of professional judgment should
be documented. The interdisciplinary
team evaluating the land health
standards is also responsible for the
adequacy of the available information. If
the interdisciplinary team concludes
that there is inadequate information
available to evaluate the land in light of
the standards, then they are directed to
begin gathering the information needed.
Various BLM technical references, such
as TR 1730–1 ‘‘Measuring and
Monitoring Plant Populations,’’ TR
1730–2 ‘‘Biological Soil Crusts: Ecology
and Management,’’ and TR 1734–4
‘‘Sampling Vegetation Attributes’’
provide descriptions of the approved
techniques for collecting data. These
technical references are available at the
BLM’s National Science and Technology
Center at https://www.blm.gov/nstc/
library/techref.htm. As new information
becomes available, it may be considered
for incorporation into public land
management policies and technical
references. When determining in what
circumstances to use a CX or an
environmental document, the
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Responsible Official has discretion to
determine, consistent with BLM
guidance, what data is sufficient to
support a finding.
Comment: Some comments state,
‘‘* * * there is significant variation in
land health standards and how they are
applied between [f]ield [o]ffices. Only in
an EA or EIS can the public be ensured
that the BLM is using current and
adequate science.’’
Response: Federal Regulations (43
CFR part 4180) and policy in the BLM’s
Rangeland Health Standards Handbook
(H–4180–1) provide for variation in land
health standards and how they are
evaluated because of inherent variability
among the ecosystems in the states
where the BLM manages public land.
For example, the Sonoran Desert is
significantly different than the Snake
River Plain. Responsible Officials have
discretion to determine, consistent with
BLM guidance, how to determine land
health status and causal factors where
standards are not achieved. Further
information regarding the
methodologies employed may be found
at the BLM’s National Science and
Technology Center at https://
www.blm.gov/nstc/library/techref.htm.
The public has opportunities outside
the NEPA process to review information
used as the basis for grazing decisions,
including scientific information. For
example, the Grazing regulations at 43
CFR 4130.3–3(b) direct: ‘‘To the extent
practical, during the preparation of
monitoring reports that evaluate
monitoring and other data that the
Responsible Official uses as a basis for
making decisions to increase or decrease
grazing use, or otherwise to change the
terms and conditions of a permit or
lease, the Responsible Official will
provide [the interested public] an
opportunity to review and offer input.’’
Comment: Some comments pointed
out ‘‘there is still a backlog of permits
that have not received an original
NEPA, as well as a growing number of
permits that are being renewed without
an updated NEPA.’’
Response: At present, Congress has
authorized the BLM, under
Appropriations legislation (Pub. L. 108–
108, Section 325, 117 Stat. 1307–1308
(2003)), to issue grazing permits with
the same terms and conditions as
expiring permits for which NEPA
review has not been completed. Section
325 provides: ‘‘the terms and conditions
shall continue in effect under the
renewed permit or lease until such time
as the Secretary of the Interior * * *
complete[s] processing of such permit or
lease in compliance with all applicable
laws and regulations, at which time
such permit or lease may be canceled,
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suspended or modified, in whole or in
part, to meet the requirements of such
applicable laws and regulations.’’ The
BLM refers to permits issued in
accordance with this law as ‘‘backlog’’
permits until they are processed as
required. Between the beginning of
Fiscal Year 1999 and end of Fiscal Year
2005, almost 15,000 permits and leases
had expired. The BLM has processed all
of these, except for 2610, which are in
‘‘backlog’’ status. For purposes of this
action, when the BLM is completing
NEPA review and documentation, the
Responsible Official will consider
application of CX 11.9 D(11) for
issuance of grazing permits when the
specific CX criteria are met and none of
the DOI ‘‘extraordinary circumstances’’
applies. Consideration of whether or not
to use the CX will facilitate reduction of
the ‘‘backlog.’’
Comment: Some comments state that
the ‘‘BLM does not have the
institutional resources to properly
[collect current ecological site data, or]
manage and employ a monitoring
program that can correctly assess what
is actually occurring.’’
Response: The ‘‘correctness’’ of the
BLM’s assessments is a matter that can
be questioned on a case-by-case basis
under 43 CFR 4130.3–3(b) (‘‘To the
extent practical, during the preparation
of reports that evaluate monitoring and
other data * * * the authorized officer
will provide [the interested public] an
opportunity to review and offer input.’’)
Development and implementation of a
monitoring program is an issue that is
separate from the establishment of a CX.
See responses above for responses to
questions specifically regarding the
establishment of CX 11.9D(11). That
said, regardless of whether a proposed
activity is reviewed under an EA, EIS or
CX, the BLM monitors the effects of the
activities to the extent its budget allows.
Monitoring data is used in land health
assessments when it is available, but is
not required. The BLM’s program
management and associated staffing
decisions regarding the monitoring of
effects of actions taken are subject to the
appropriations process.
Comment: Some comments state that
the BLM did not begin site-specific
NEPA for grazing management until the
1990s. They cite the IBLA decision in
Oregon Natural Resources Council v.
BLM, 129 IBLA 269 (1994) where
extending a permit’s termination date or
changing the name of the permit holder
constitutes an action requiring notice
and opportunity to protest. The decision
applies to whether or not an ‘‘interested
public’’ or ‘‘affected interest’’ has the
opportunity to protest and appeal a
decision. The implied concern is that,
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by adopting the CXs 11.9D(11)–(12), the
public will be unable to protest or
appeal administrative decisions made
by the BLM.
Response: The BLM was conducting
site-specific NEPA analyses in the early
1970s to facilitate informed decisions on
the development and implementation of
grazing AMPs. Implementation of the
proposed revisions to the NEPA
management process will not affect
‘‘interested public’’ or ‘‘affected
interests’’ right to protest and appeal
BLM grazing decisions, including
decisions made following the CX review
process (43 CFR part 4160).
Comment: The same comments
express concern that, if the new grazing
permit CXs 11.9D(11)–(12) cover
administrative actions, such as changing
the termination date of the permit, sitespecific environmental analyses will not
be conducted for grazing allotments that
have yet to be given the benefit of a sitespecific review.
Response: The BLM deleted part (b) of
CX 11.9D(11) to clarify the intent of the
CX to require completion of a land
health assessment before application of
a CX to a specific allotment described in
the permit could be considered.
Therefore, the CX 11.9D(11) may only
be used for administrative changes such
as changes of names on grazing permits,
if the specific criteria for use of the CX
11.9D(11) are met. Use of the CX in
issuing such permits would be subject
to the reviews included in the CX
limitation involving the completion of
land health assessments as well as the
consideration of whether any
‘‘extraordinary circumstances’’ apply.
The BLM has decided not to finalize CX
11.9D(12).
Comment: Some comments state that
‘‘administrative action’’ is inadequately
defined, and therefore, could be
construed ‘‘to include all BLM actions.’’
Response: This comment refers to
proposed CX 11.9D(12), which the BLM
has decided not to finalize.
Comment: Some comments state that
the BLM is issuing grazing permits for
less than market value.
Response: The comment has no
bearing on the adoption of CXs.
Comment: Some comments state that
the BLM should revise the CXs to be
more specific relative to the stipulation
relating to livestock being ‘‘solely’’
responsible for the failure to meet land
health standards.
Response: The language for CX
11.9D(11) has been revised to clarify the
limitation. It now reads, ‘‘Not meeting
land health standards due to factors that
do not include existing livestock
grazing.’’
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Responses to Specific Comments on
Section 11.9—Categorical Exclusions
G. Transportation (Sub-Parts G(1)–(4))
G(1)–(3)—Comments.
Comment: Some comments state that
the modified transportation CXs
11.9G(1)–(3) make no distinction among
motorized, mechanized, and foot/horse
trails, or between authorized and
unauthorized roads and trails.
Response: The comments are correct.
These CXs do not address the type of
use authorized on a road or trail. Trail
use is authorized through the land use
planning process. These CXs address
actions, which take place following this
planning process, and are primarily
concerned with identification within a
transportation plan, routine
maintenance or temporary closures.
Further, the Responsible Official
reviews each proposed action as to
whether any of the ‘‘extraordinary
circumstances’’ in 516 DM 2.3A(3) and
appendix 2 apply. If any ‘‘extraordinary
circumstance’’ applies, the revised
transportation CXs 11.9G(1)–(3) may not
be used.
Comment: Some comments state that
the BLM fails to account for important
differences between roads and trails.
Response: The BLM guidance
(Washington Office Instruction
Memorandum No. 2006–173) defines
similar routine management and
maintenance requirements for roads and
trails. Engineering, design and signing
requirements are consistent between
roads and trails, and should be
consistently addressed in the NEPA
context. Trails, like roads, require
maintenance (e.g., erosion control,
stabilization, and signs) and are
periodically closed for safety or resource
protection purposes. The major
difference between roads and trails is
their spatial footprint and degree of
infrastructure design, which is less for
trails than for roads. With respect to
trail location and design, as with respect
to roads, the BLM considers resource
conditions in design and placement
decisions. The BLM’s State Trails and
Travel Management Leads confirmed
that, based upon their past observations
and professional experience,
implementation of past actions covered
under the existing CX did not result in
significant effects, individually or
cumulatively. In addition, the BLM’s
Trails and Travel Management Leads
agreed that based on their experiences,
the environmental effects of these
actions along trails as proposed and
finalized in the establishment of CXs
11.G(1)–(3) will not result in a
significant effect, individually or
cumulatively. Further, regardless of
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whether the transportation feature is a
road or a trail, all proposed actions
possible under the CXs would be
reviewed against the DOI ‘‘extraordinary
circumstances’’ (516 DM 2 and
appendix 2). If any apply, the CXs could
not be used; rather, an EA or EIS would
be prepared.
Comment: Some comments ask that
the BLM not add ‘‘trails’’ to the existing
transportation CXs 11.9G(1)–(3).
Response: See response above.
Further, it is appropriate to consider
roads and trails together in
transportation management and
maintenance, which are the activities
addressed by CXs 11.9G(1)–(3).
Collectively roads and trails form the
travel network in a management area.
Both roads and trails require signs,
markers, culverts, and other similar
structures covered by CX 11.9G(2).
Trails, like roads, occasionally need to
be closed or barricaded, which is the
subject of CX 11.9G(3). The addition of
trails to CXs 11.9(G)(1)–(3) is consistent
with the BLM’s management practices
and comprehensive planning for roads
and trails-related activities. These
management practices and planning
considerations are guided by regulation
(43 CFR 8342.2 ‘‘Designation
Procedures’’—including ‘‘identification
of designated areas and trails’’), BLM
directives and guidelines (BLM Manual
9130 (June 7, 1985)), BLM Land Use
Planning Handbook (H–1601–1), and
current BLM Sign Manual 9130.
Coverage of minor management
activities by these three CXs will enable
more timely day-to-day management
responses, which directly benefit the
environment and/or assist in visitor
safety and result in no significant
impact.
Comment: Some comments ask that
the BLM clarify the meaning of the
modifier ‘‘existing’’ in the transportation
CXs 11.9(G)(1) and 11.9(G)(2).
Response: The term ‘‘existing’’ has
been replaced by ‘‘eligible’’ to clarify
that any roads and trails to be addressed
by the CXs 11.9(G)(1) and (2) must meet
certain requirements established in the
land use and transportation planning
processes. The requirement criteria for
defining a road or trail as open are
developed as part of the land use
planning process to meet resource
management objectives. The word
‘‘existing’’ was replaced with the word
‘‘eligible’’ to avoid confusion with the
BLM’s OHV designation of ‘‘Limited.’’
Comment: Some comments state that
it is inappropriate to treat routine
installation of signs, markers, culverts,
ditches, waterbars, gates, or cattleguards
as equally benign when analyzing
potential environmental effects which
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the BLM has done in proposing the
11.9G(2) CX.
Response: Based upon field
experience, implementing the category
of actions, as defined in the CX, has not
resulted in individually or cumulatively
significant effects for or along roads.
The BLM State Trail and Travel
Management Leads have concluded
based upon years of professional
experience that the addition of ‘‘trails’’
to these categories will not result in
individually or cumulatively significant
environmental effects. The BLM did not
propose changes to the overall category
of activities covered by the existing CX
11.9G(2) for management actions for and
along roads, rather it added to the
ability of the BLM to implement the
activities along the smaller linear trail
features. The BLM is adding trails to the
CX to more accurately reflect the
similarities in the management actions
and maintenance requirements under
these categories for roads and trails and
due to their similar non-significant
environmental effect.
Comment: Some comments state that
by including existing trails, the BLM
could be permitting approval and
signing of illegally created motorized
trails or providing access or use rights
to third parties, and the BLM will
encourage additional use of
unauthorized trails.
Response: The term ‘‘existing’’ has
been replaced by ‘‘eligible’’ to clarify
that all roads and trails that can be
addressed by the CXs must meet certain
requirements under the land use and
transportation planning processes.
Decisions regarding the designation of
roads and trails, determinations of OHV
open, closed or limited areas, or
‘‘formal’’ recognition of the roads and
trails contained within any
transportation system are determined
through the appropriate land use
planning or activity planning that is
accompanied by a NEPA review process
(see the BLM Land Use Planning
Handbook H–1601–1, appendix C,
Section D). These decisions are not
determined through application of the
CX.
Responses to Specific Comments on
Section 11.9—Categorical Exclusions
H. Recreation Management (Sub-Part
H(1))
H(1)—Comments.
Comment: Some comments state that
the analysis used to justify the special
recreation permit (Recreation
Management ) CX 11.9H(1) is flawed
because it ‘‘assumes that [the] BLM
review process will ensure categorical
exclusions will not be used where
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significant consequences may ensue, a
rationale that the courts have rejected.’’
Response: The comment is not clear
about which court has ‘‘rejected’’ the
‘‘rationale’’ that CXs ‘‘will not be used
where significant consequences may
ensue.’’ The CEQ regulations (40 CFR
1508.4 and 1507.3) authorize federal
agencies to establish and apply CXs and
specify that CXs will not be applicable
when there are extraordinary
circumstances. The BLM followed CEQ
regulations in proposing additional CXs
to reduce paperwork and delays (40 CFR
1500.4 and 1500.5) and enable the BLM
to concentrate on environmental issues
that are associated with proposed
actions that require further analysis in
an EA or an EIS. Supporting
documentation for the revised
Recreation Management CX 11.9H(1)
was reviewed to determine whether
there is sufficient evidence based on
past NEPA analyses and subsequent
review of environmental effects to
support the finding that the activity
included in the proposed CX would not
cause individually or cumulatively
significant environmental impacts. The
establishment of CXs has been upheld
in Heartwood, Inc. v. U.S. Forest
Service, 73 F. Supp. 2d 962, 972–73
(S.D. Ill. 1999), aff’d 230 F.3d 947, 954–
55 (7th Cir. 2000). The BLM
administrative review concluded that
special recreation permits (SRP) that
meet the criteria of the CX, will not
result in individually or cumulatively
significant effects. In addition, activities
conducted through the CX review
process must address the ‘‘extraordinary
circumstances’’ (516 DM 2.3(A) and
appendix 2) and be consistent with all
applicable laws and requirements
imposed for protection of the
environment.
Comment: The same comments state,
‘‘although CEQ regulations require that
CXs incorporate an ‘extraordinary
circumstances’ exception, 40 CFR
1508.4, the presence of the exception is
not an excuse for the authorization of
otherwise improper or inadequately
justified CXs. See Heartwood, Inc. v.
United States Forest Service, 73 F.
Supp. 2d 962, 976 (rejecting as
‘‘circular’’ the Forest Service’s argument
that exceptional circumstances
exception adequately compensates for
failure to consider cumulative effects of
an action proposed for categorical
exclusion).’’
Response: See previous response
relative to the court case cited. In
addition, the facts in the Heartwood
decision are distinguishable from those
underlying the proposed actions here;
therefore, they do not apply in this
context. The BLM has established the
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Recreation Management CX 11.9H(1),
based on data gathered and reviewed
using generally accepted analytic
procedures. Furthermore, the BLM’s
analysis included a review of NEPA
documents which themselves included
analyses of cumulative effects and the
subsequent BLM review of the actual
effects. A statistically valid random
sample of the BLM’s total population of
SRP records indicates that 84 percent of
the BLM’s SRPs have had no
unanticipated individual or
cumulatively significant impacts. Upon
further review, the BLM clarified the CX
language to include the limitation that
the CX cannot be applied to commercial
boating activities proposed along
designated Wild and Scenic Rivers. This
limitation was added in accordance
with CEQ proposed guidance on the
establishment and use of categorical
exclusions (71 FR 54816, September 19,
2006), which encourages agencies to
clearly define the category of actions
covered, as well as any physical or
environmental factors that would
constrain its use. These constraints
ensure that the SRPs likely to have
significant effects would not be eligible
for CX use. Therefore, the SRP activities
that could be covered under the CX by
meeting all CX criteria, would not result
in a significant effect on the
environment either individually or
cumulatively. The BLM mandates that
proposed actions or activities be, at a
minimum, consistent with the DOI and
the BLM regulations, manuals,
handbooks, policies, and applicable
LUPs regarding design features, best
management practices, terms and
conditions, conditions of approval, and
stipulations. The BLM requires that all
SRP permittees must agree to comply
with the specific SRPs terms and
conditions identified on the BLM Form
2930–1, which the BLM uses
nationwide. Additional examples of
standard stipulations, terms, conditions
of approval and specific limitations to
apply to SRPs can be found in the
BLM’s Recreation Permit Handbook (H–
2930–1 appendix C). An example of one
state-specific guidance is the Wyoming
Statewide Recreation Permit Handbook
(2932–WY–050–SRP–03–05). The BLM
must review all proposed actions
against the DOI list of ‘‘extraordinary
circumstances’’ (516 DM 2.3A(3) and
appendix 2). If one or more of the
‘‘extraordinary circumstances’’ apply,
the CX could not be used; rather, an EA
or EIS would be prepared.
Comment: Some comments state that
the analysis used to justify Recreation
Management CX 11.9H(1) is ‘‘flawed’’
because it ‘‘fails to distinguish between
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significantly different categories of
activities, such as motorized versus nonmotorized recreation events.’’ In other
words, it exempts a ‘‘category of
actions’’ without any analysis of the
actions, which belong to that category.
Response: The BLM disagrees. The
CEQ regulations (40 CFR 1508.4 and
1507.3) authorize Federal agencies to
establish and apply CXs to categories of
actions that do not have significant
effects, either individually or
cumulatively, on the quality of the
human environment, and specify that
CXs will not be applicable when there
are extraordinary circumstances. The
BLM examined, collectively SRP
activities authorized in LUPs, and found
that for this category of action, with the
added limitation respecting commercial
boating along Wild and Scenic Rivers,
there were no significant impacts,
individually or cumulatively. This
category of actions, the authorizing of
SRPs, includes permitting commercial
recreation operations, competitive
events and organized group activities, as
stated on page 2 of the SRP analysis
report available at https://www.blm.gov/
planning/news.html. As such, the
category includes all types of
recreational activities engaged in by the
public. The report lists, for instance, an
organized group of bird watchers and an
endurance horse racing event, but as
stated in the report the recreational
activities covered by SRPs are not
limited to the examples given. The SRPs
are also granted for mechanized and
motorized recreational activities. The
SRP data analyzed incorporated all
types of recreational activities
authorized under SRPs, including those
issued for motorized recreational
activities. For additional information
regarding the definition of these
activities, see 43 CFR 2932. Further,
with respect to the grant of each SRP,
the Responsible Official must require
the standard terms and conditions
found on Form 2930–1 and must
address whether any ‘‘extraordinary
circumstances’’ (516 DM 2 and
appendix 2) apply. If any of the
‘‘extraordinary circumstances’’ apply,
the CX cannot be used.
Comment: Some comments state that
the analysis used to justify the SRP CX
11.9H(1) is ‘‘flawed’’ because using a
history of EA process review data to
justify the CX fails entirely to take into
consideration the extent to which
adverse environmental consequences
are identified and avoided through the
EA process and accompanying public
involvement.
Response: The BLM disagrees. The
CEQ regulations (40 CFR 1508.4 and
1507.3) authorize Federal agencies to
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establish and apply CXs. The BLM
followed CEQ regulations in proposing
additional CXs to reduce paperwork and
delays (40 CFR 1500.4 and 1500.5) and
enable the BLM to concentrate on
environmental issues associated with
proposed actions that require further
analysis in an EA or EIS. The Recreation
Management CX 11.9H(1) was subjected
to administrative review to determine
whether there is supporting evidence
based on past NEPA analyses, as well as
evaluation of environmental effects of
the action as implemented, sufficient to
support the conclusion that this
category of action does not cause
individually or cumulatively significant
environmental impacts. The BLM found
no significant effect for all cases except
commercial boating activities along
Wild and Scenic Rivers. Based upon
further review, and in accordance with
CEQ proposed guidance on the
establishment and use of categorical
exclusions (71 FR 54816, September 19,
2006), which encourages agencies to
clearly define the category of actions
covered, as well as any physical or
environmental factors that would
constrain its use, the final SRP CX
includes a limitation on this type of SRP
so that the CX cannot be used for
consideration of commercial boating
SRPs along Wild and Scenic Rivers.
Further, the BLM must review proposed
actions considered for use of a CX
against the DOI ‘‘extraordinary
circumstances’’ (516 DM 2.3A(3) and
appendix 2). If one or more of the
‘‘extraordinary circumstances’’ apply,
the CX cannot be used. In authorizing
an action, regardless of the type of
NEPA compliance completed, the BLM
may not violate any applicable Federal,
State, local, and tribal laws and
requirements imposed for protection of
the environment. The establishment of
CXs have been upheld in Heartwood,
Inc. v. U.S. Forest Service, 73 F. Supp.
2d 962, 972–73 (S.D. Ill. 1999), aff’d 230
F.3d 947, 954–55 (7th Cir. 2000). In
addition, public involvement has been,
and remains, critical to the BLM
decision-making process. The public
will continue to have opportunities for
involvement during the development of
LUPs and activity plans. Furthermore,
in instances where there is a high public
interest in an individual proposed SRP,
the Responsible Official retains the
discretion to involve the public
throughout the decision-making process
regardless of the kind of NEPA review
conducted.
Comment: Some comments state that
the ‘‘best outcome’’ would be to retain
the SRP CX 11.9H(5) and modify and
adopt the new CX 11.9H(1) by ‘‘adding
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a ceiling or maximum number of people
and/or vehicles that may participate in
the recreational activity or event, in
addition to any time an[d]/or acreage
limits.’’
Response: The Recreation Program
determined that the existing CX needed
to be revised to clarify the language to
ensure consistent application of its use
Bureau-wide. The new language
approved for the CX 11.9H(1) was
developed following generally accepted
analytical procedures. The proposed
language did not include ceilings or
maximum numbers of people and/or
vehicles that may participate in
activities addressed by the CX because,
for the overwhelming number of SRPs
issued and otherwise meeting the
proposed criteria, the NEPA analyses
conducted resulted in FONSIs
regardless of the number of people or
vehicles involved in the permitted
activity and the subsequent BLM review
of the actual effects confirmed there
were no significant impacts. In addition,
the BLM has added limits to the final
CX language to clarify that it cannot be
applied for the permitting of
commercial boating along Wild and
Scenic Rivers, the only type of SRP
sampled that was found to have or
potentially have significant
environmental effects, rendering it
unacceptable for CX consideration.
Further, if needed, establishment of
visitor use limitations or vehicle
number limitations are determined
during the land use planning process.
Based on BLM data, when the new
Recreation Management CX 11.9H(1)
criteria are met, individual and
cumulatively significant impacts will
not occur. The staging area acre
limitation was determined during the
analytical process, based on the
professional judgment of the BLM
recreation specialists and their review of
past SRP activities, to be an appropriate
threshold to set to ensure that
significant effects do not occur for
future actions addressed by the CX.
Comment: Some comments ask the
BLM to retain the existing CX ‘‘in lieu
of this new H(1)CX,’’ because they
prefer the concluding phrase ‘‘similar
minor events’’ which is an important
and ‘‘reasonable’’ limitation.
Response: See response above. The
new language is based on a completed
NEPA review process that included data
collected through a stratified random
sample of all SRPs issued by the BLM
from October 1, 2000, through
September 30, 2005. The analysis of this
sample supports the new Recreation
Management CX 11.9H(1).
Comment: Some comments wanted
the CX 11.9H(1) to apply ‘‘to the
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relatively low-impact examples
provided’’ and not allow ‘‘other
activities, with extremely serious
adverse environmental consequences,
such as motorized vehicle races and
events and activities on Wild and
Scenic Rivers.’’
Response: Upon further review, the
BLM has added a limitation to the terms
of the CX. The CX may not be used in
the permitting of commercial boating
activities on Wild and Scenic Rivers as
this was the one type of SRP activity
sampled that resulted in a significant
effect. None of the other SRP activities
sampled during the establishment of
this CX resulted in environmentally
significant effects, individually or
cumulatively. As to the commenter’s
other concern, while the list of
examples provided in the December 12,
2005, CX Project—Recreation analysis
report (available at https://www.doi.gov/
oepc/cx_analysis.html and https://
www.blm.gov/planning/news.html) did
not include motorized vehicle activity
examples, it was not an exhaustive list.
In fact, SRPs authorizing motorized
activities were included in the sampled
data, which reflected all types of SRPs
authorized. Recreational activities of
any type with ‘‘extremely serious
adverse environmental consequences’’
as mentioned in the comment, would
not be reviewed using a CX as one or
more of the ‘‘extraordinary
circumstance’’ would apply (516 DM
2.3A(3) and appendix 2). If any of the
‘‘extraordinary circumstances’’ apply,
the CX will not be used, and an EA or
EIS would be prepared.
Comment: Some comments ask if CX
11.9H(1) covers ‘‘organized and/or
commercial events.’’
Response: Yes, CX 11.9H(1) covers all
types of SRPs, including organized and/
or commercial events, that meet the CXspecific criteria and where none of the
‘‘extraordinary circumstances’’ apply
(516 DM 2.3A(3) and appendix 2).
Comment: Some comments state that
CX 11.9H(1) ‘‘time and space
limitations’’ are not enough to ‘‘negate
the environmental impacts’’ and
‘‘concentrating [any] such activities to a
confined space can further and
substantially increase the impacts.’’
Response: The BLM disagrees. The
‘‘time and space’’ limitations set in
establishment of the proposed CX were
derived based on the administrative
review described in the analysis report
for the SRP CX found at https://
www.blm.gov/planning/news.html.
Upon further review, the BLM has
decided to change the limitation for the
Recreation Management CX 11.9H(1)
length of overnight stay from 7 to 14
consecutive nights to provide
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consistency with the typical length of
stay for any casual visitor using public
lands (43 CFR 8364; 8365.1–2
‘‘Occupancy and Use,’’ and 8365.1–6
‘‘Supplementary Rules’’). Additional
review of the data analyzed during the
establishment of the CX confirmed that
there was no difference in results of the
NEPA review with respect to SRPs with
overnights stays of up to 7 nights, as
compared to stays of up to 14 nights.
Significant environmental effects did
not result from SRPs with lengths of
stays of up to 14 nights. The acre limit
was set during the establishment of the
proposed CX based on the professional
judgment of the BLM recreation
planners and their review of SRP
activities. This acreage was refined for
the final CX based on the data reviewed.
The BLM professional judgment,
supported by the data analysis ensures
that no significant impact will occur
based on implementation of this
limitation for this CX.
Comment: Some comments state that
the analysis used to justify the CX is
‘‘flawed’’ because it ‘‘fails entirely to
address the question of cumulative
impacts on the environment.’’
Response: See above responses
regarding establishment of the
Recreation Management CX. None of the
projects reviewed that meet the final CX
language criteria, resulted in
cumulatively significant environmental
effects. Further, all proposed SRPs
considered for application of the CX
would be reviewed against the
‘‘extraordinary circumstances’’ (516 DM
2.3A(3) and appendix 2), and
extraordinary circumstance 2.6
specifically addresses cumulative
impacts on the environment.
Comment: Some comments state that
CX 11.9H(1) ‘‘should not be adopted as
written’’ and that the CX should
‘‘exclude activities that utilize
motorized equipment, which
intrinsically have the potential to cause
significant environmental impacts.’’
Some comments ask the BLM to exclude
‘‘off-highway vehicles and motorized
recreation’’ because they cause
significant impacts, such as increased
noise levels, air pollution from dust and
fumes, and incidental off-road use.
Response: See above responses. The
data analyzed during the establishment
of the CX included ‘‘off-highway vehicle
and motorized recreation’’ activities.
The BLM concluded based on the data
analyzed, that the SRPs covered under
the CX did not result in significant
environmental effects, individually or
cumulatively. Further, CX 11.9H(1) can
only be used to permit recreational
activities that meet the CX criteria when
none of the ‘‘extraordinary
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circumstances’’ (516 DM 2.3A(3) and
appendix 2) apply. If any ‘‘extraordinary
circumstances’’ apply, the CX cannot be
used.
Comment: Some comments state that
not all types of recreation use/activity
should be eligible for the Recreation
Management CX 11.9H(1), even if the
use/activity meets the area and number
of consecutive nights criteria. For
example, certain recreational uses, such
as cattle drives, rodeos, and motorcross
and motorcycle hill climbing events,
may have significant effects. Federal
court cases and the ‘‘IBLA have
specifically found [these kinds of
events] to have significant (and adverse)
effects * * * .’’
Response: The BLM used analytical
procedures to examine the NEPA
process results used to issue 8,063 SRPs
from October 1, 2000, through
September 30, 2005. The BLM currently
issues an estimated 3,500 SRPs
annually, of which approximately 1,500
permits are re-issued each year. The
permits granted include SRPs for the
types of recreation actions identified by
the comments. The BLM examined,
collectively, SRP activities authorized in
LUPs, and found that for this category
of action, with the added limitation
pertaining to commercial boating on
Wild and Scenic Rivers, there are no
significant environmental effects, either
individually or cumulatively. This
category of actions, the authorizing of
SRPs, includes permitting commercial
recreation operations (excepting boating
along Wild and Scenic Rivers),
competitive events and organized group
activities, as stated on page 2 of the SRP
analysis report available at https://
www.blm.gov/planning/news.html. As
such, the category includes all types of
recreational activities engaged in by the
public. The report lists, for instance, an
organized group of bird watchers and an
endurance horse racing event, but as
stated in the report the recreational
activities covered by SRPs are not
limited to the examples given. These
SRPs are also granted for mechanized
and motorized recreational activities.
The SRP data and activities analyzed
included all types of recreational
activities authorized under SRPs. For
additional information regarding the
definition of these activities, see 43 CFR
2932. Based on a statistically valid
sample of SRPs issued, the BLM has
determined that establishment of the
new SRP CX is warranted; all types of
recreation activities that meet the CX
criteria are eligible for authorization
under the new SRP CX. However, if any
of the DOI ‘‘extraordinary
circumstances’’ (516 DM 2.3A(3) and
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appendix 2) apply, the CX cannot be
used.
Comment: Some comments wanted to
know if ‘‘the 3% of SRPs with
significant impacts’’ involved motor
vehicle events and whether the SRP
data can be used to differentiate
between significant impacts associated
with different types of SRP activities.
Response: The BLM data reviewed
revealed that the 3% of the SRPs with
significant impacts were for SPR
commercial boating activities along
Wild and Scenic Rivers. Therefore, the
BLM added a specific limitation to the
CX so that it cannot be used for
commercial boating along Wild and
Scenic Rivers. None of the remaining
SRPs activities sampled resulted in
significant environmental effects,
individually or cumulatively.
Comment: Some comments wanted
the BLM to limit the number of
motorized vehicles used, duration,
speed, or type of event and/or to
specifically address the different
impacts from the volume of users,
intensity of use, and equipment
involved.
Response: None of the SRP activities
that meet the final CX criteria resulted
in significant environmental effects,
individually or cumulatively. Therefore,
the BLM did not add additional
limitations to the CX as suggested in the
comment.
Comment: Some comments asked the
BLM to describe how the size of the ‘‘3
contiguous acres’’ and the seven
consecutive day and overnight stay
limits were derived.
Response: Data analyses revealed no
statistical relationship between the size
of the staging area, number of
consecutive overnights permitted, and
the incidence of significant individual
or cumulative impacts. Therefore, the
BLM selected the three contiguous acre
area limit based upon a review of the
SRPs issued. Of 548 informative
responses to a questionnaire about the
actual size of the staging area and
number of nights involved in the SRPs
issued, 90 percent of the SRPs with
staging area information reported that
the area involved was equal to or less
than 3 acres. The 7-day stay limit was
derived by analyzing the entire
population of SRPs in the BLM’s
Recreation Management Information
System and taking the average length of
stay permitted. Based on comments
received and the fact that the data
revealed no relationship between length
of overnight stay and significant
impacts, the BLM has decided to change
the Recreation Management CX 11.9H(1)
length of overnight stay from 7 to 14
consecutive nights to provide
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45533
consistency with the allowable length of
stay for any casual visitor using public
lands (43 CFR 8364, 8365.1–2
‘‘Occupancy and Use,’’ and 8365.1–6
‘‘Supplementary Rules’’). This is to
ensure equality regarding ‘‘length of
stay’’ limitations between permitted use
activities and the casual use activities
on public lands.
Comment: Some comments express a
concern that the three contiguous acres
language could be variously interpreted
because it is not clear whether the
activity area includes a linear route,
such as a race. They suggested adding
the words ‘‘staging area’’ to clarify the
CX language.
Response: The BLM agrees. The word
‘‘contiguous’’ has been deleted and the
term ‘‘staging area’’ has been added to
the CX to clarify the intent of the
limiting condition. See staging area
definition below.
Comment: Some comments ask that
the BLM define ‘‘staging area.’’
Response: A staging area is defined in
this context as an area where use is
concentrated, usually to enable access to
a recreational activity that involves
traveling across public lands along
roads, trails or in areas authorized in a
LUP. Examples include trailheads,
gathering points, base or hunting camps,
boat launching or parking areas, and the
like. Other examples of staging areas
include a congregation point (e.g., for
parking) where a group activity begins
and/or ends, a viewing area for an event,
a training course or play area not
involving existing roads or trails. The
staging area acreage amount does not
include the use of authorized roads,
trails or access to adjacent areas open
for recreational use in the LUP.
Comment: Some comments ask that
the BLM define ‘‘travel management
area’’ and ‘‘travel networks.’’
Response: ‘‘Travel management areas’’
and ‘‘networks’’ are defined in the
BLM’s Land Use Planning Handbook
(H–1601–1 appendix C and Glossary
page 8). ‘‘Travel Management Areas’’ are
defined as polygons or delineated areas
where a land use planning process has
classified areas as open, closed, or
limited to off-highway vehicle use or
other modes of travel. The terms ‘‘travel
management area’’ and ‘‘networks’’ were
replaced in the final CX language with
‘‘recreational travel along roads, trails or
in areas authorized in a LUP’’ to clarify
the intent of the final CX.
Comment: Some comments ask for
more information on how the BLM: (a)
Differentiates organized/commercial
groups relative to private/individual use
in the travel management and
transportation network planning
context; (b) deals with permitted
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dispersed recreational activities
impacts; and (c) manages events with
large staging areas on private lands
supporting permitted recreational use of
public lands.
Response: (a) The BLM differentiates
SRP authorized activities from private/
individual use (i.e. casual use) based on
definitions found in 43 CFR 2930 and
the BLM guidance in the BLM
Recreation Permit Handbook (H–2930–
1, pages 10–12). (b) The BLM does not
differentiate between dispersed or nondispersed recreational activity impacts
when considering a proposed SRP
action. The BLM considers whether the
proposed activity meets the criteria set
forth in the CX and if not, a different
type of NEPA review would be
conducted to determine the
environmental effects of the proposed
SRP. In addition, general dispersed
recreational activity impacts would be
analyzed during the land use planning
process. (c) The BLM SRPs are use
authorizations for activities on the BLMadministered public lands and related
waters. The issuing of SRPs for events
involving ‘‘staging areas’’ on private
lands are coordinated by the BLM with
stipulations requiring the permittee
collaborate with appropriate private
landowners and/or public agencies (law
enforcement, highway, fish and game,
etc., BLM Form 2930–1, Special
Recreation Application and Permit). If
significant impacts, as revealed in the
course of ‘‘extraordinary circumstances’’
review, may occur from issuance of an
SRP, this CX could not be used.
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Responses to Specific Comments on
Section 11.9—Categorical Exclusions
I. Emergency Stabilization (sub-part I(1))
I(1)—Comments.
Comment: Some comments state that
the Emergency Stabilization CX is (1)
too broad, (2) based on subjective
criteria, and (3) includes far too many
acres of land disturbance.
Response: (1) The new Emergency
Stabilization CX builds on the existing
DOI CX that addresses post-fire
rehabilitation responses to wildfires
(516 DM 2 appendix 1, section 1.13,
Finalized at 68 FR 33814, June 5, 2003).
Post-fire rehabilitation activities as
defined in the DOI CX refer to response
activities taken within 1 to 3 years
following a wildfire. For the purposes of
this BLM-specific CX, emergency
stabilization response activities are the
same on-the-ground treatments as the
post-fire rehabilitation treatments but
they must occur within one year of the
natural land disturbance event. The
events may include destabilizing natural
events, such as wildfire, floods, strong
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weather, earthquakes, and landslips.
The emergency stabilization response
activities include management
treatments, which are prescribed to
minimize threats to life or property and
to stabilize and prevent unacceptable
degradation of natural and cultural
resources as a result of a natural land
disturbance event. The emergency
stabilization responses under this CX
are the same as the DOI CX post-fire
rehabilitation activities and may
include: Seeding to prevent erosion or
the spread of noxious weeds;
installation of structures, such as log
erosion barriers or straw wattles; felling
hazard trees along roads or in
campgrounds; and similar treatments to
prevent or minimize negative impacts
caused by a natural land disturbance
event. While the natural events
responded to by activities covered
under this CX may be different from a
wildland fire, because the response
actions taken under this CX are
generally the same as those taken under
the DOI CX for post-fire rehabilitation,
the BLM has concluded that, similarly,
they do not result in significant effects,
individually or cumulatively. The BLM
reached this conclusion on the basis
both of conducting a review of the
wildfire data, and based on the
professional judgment of BLM
specialists experienced with these types
of events and response activities and
their effects. Appropriate use of the
Emergency Stabilization CX 11.9I(1) is
warranted on the basis of this review
and judgment, as well as because such
use will be in accord with current
administrative procedures such as the
following: BLM Burned Area Emergency
Stabilization and Rehabilitation
Handbook (H–1742–1); specific
standards and guidelines expressed in
policy documents such as Instruction
Memorandum 2006–162; and the
specific terms and conditions identified
within local LUPs. Further, the BLM
must review all proposed emergency
stabilization treatment against the DOI’s
‘‘extraordinary circumstances’’ (516 DM
2.3A(3) and appendix 2). The CX cannot
be used if any of the ‘‘extraordinary
circumstances’’ apply.
(2) The category of actions covered by
the new Emergency Stabilization CX, as
well as its specific criteria, were derived
from a review of approximately 300
post-fire emergency stabilization/
rehabilitation projects analyzed during
the establishment of the DOI post-fire
rehabilitation CX 620 DM Ch 3.3E, June
5, 2003. Information on 30 variables was
collected and analyzed. These data
included project-specific information on
the location, project size, vegetation
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type, emergency stabilization/
rehabilitation treatments performed, the
type of NEPA review performed,
predicted environmental impacts of
proposed treatments and the actual
environmental impacts after treatments.
The criteria applied were not
subjectively derived. In the judgment of
the BLM professionals experienced in
implementing these activities, the
activities and their effects for which the
BLM Emergency Stabilization CX is
proposed, are of the same nature as the
activities and their effects analyzed as
the basis for establishment of the DOI
post-fire rehabilitation CX.
(3) The 4,200-acre limit was derived
through analysis of the DOI CX data set,
which represents a range of
environments in which wildfire events
routinely occur on public lands. This
CX adopts the 4,200-acre limit to
maintain consistency with the DOI CX
limitation as the effects of the actions
taken in response to wildfires. These
response actions are the same as those
taken in response to other natural land
disturbance events. Based on review of
the DOI CX data by professionals in the
area of post-disturbance stabilization,
the BLM concludes that this CX will not
have individual or cumulative
significant impacts when all conditions
of the CX were met. Further, as an
additional safeguard, the BLM must
review all proposed actions against the
DOI ‘‘extraordinary circumstances’’ (516
DM 2.3A(3)). If any of the
‘‘extraordinary circumstances’’ apply,
the CX cannot be used.
Comment: Some comments state that
post-emergency treatments ‘‘merit
thorough analysis regarding potential
significant impacts.’’ Affected areas are
‘‘often extremely vulnerable to further
environmental damage’’ and ‘‘the
activities included do not necessarily
work successfully to mitigate damages
from natural events and often cause
adverse impacts on their own.’’
Response: The DOI post-fire
rehabilitation CX data review concluded
that no significant individual or
cumulative impacts are likely to occur
as a result of the types of stabilizing
response activities that are taken within
1 to 3 years of the natural disturbance
event. The BLM’s Emergency
Stabilization CX includes an additional
limitation that actions can only be taken
within one year following the natural
disturbance event. In addition, the
Emergency Stabilization CX cannot be
used if one or more of the DOI
‘‘extraordinary circumstance’’ (516 DM
2.3A(3) and appendix 2) applies.
Comment: Some comments ask that
the BLM ‘‘consider alternatives [to
repair or replacement of roads and
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culverts] that would permit
improvement of wildlife habitat or
watershed condition.’’
Response: The CX 11.9I(1) may be
used only for Emergency Stabilization
treatments when the CX specific criteria
are met in full. Further, each proposed
action must be reviewed against the DOI
‘‘extraordinary circumstances,’’ if any
apply, the CX cannot be used.
Emergency stabilization activities are
those treatments that are prescribed to
minimize threats to life or property and
to stabilize and prevent unacceptable
degradation of natural and cultural
resources as a result of a natural land
disturbance event. The emergency
stabilization actions must be taken
within one year following the
disturbance event. The emergency
stabilization activities may include:
seeding to prevent erosion or the spread
of noxious weeds; installation of
structures, such as log erosion barriers
or weed-free straw wattles and fish
friendly culverts; felling hazardous trees
along roads or in campgrounds; and
similar treatments to prevent or
minimize negative impacts caused by
certain inevitable natural events. These
activities are covered under CX 11.9I(1)
because they are commonly accepted
minimum impact responses to the
effects of floods, weather events,
earthquakes, and landslips in addition
to wildfires. Improvements to natural
resource conditions may be a derived or
incidental benefit, but cannot be a
driving purpose for the proposed action
for use of this CX.
Comment: Some comments ask that
the BLM clearly define what constitutes
‘‘temporary road’’ construction to
‘‘minimize * * * impacts,’’ and to
include language in each CX that
provides a requirement that temporary
roads be obliterated when a project is
completed. Some comments suggested
that road construction should only be
carried out following a detailed
analysis.
Response: The need for temporary
roads is determined during the project
proposal process. The Responsible
Official is required to review the project
proposal against the DOI’s extraordinary
circumstance (516 DM 2.3A(3) and
appendix 2). Project proposals include
descriptions of when vehicle and
equipment access is necessary, how it
will be done, and, if temporary roads are
included, how they are to be reclaimed.
Based on the DOI CX data analyzed for
the proposed Emergency Stabilization
CX (11.9I(1)), there are no individual or
cumulatively significant environmental
effects when temporary roads are part of
activities identified in the CX. The BLM
added a definition to the CX language to
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clarify what a temporary road is for use
under this CX. Further, if one or more
of the ‘‘extraordinary circumstances’’
apply the CX cannot be used.
Comment: Some comments
recommend that culvert repair and
replacement not be included in the list
of exempted treatments and that the CX
language be changed to limit treatments
to ‘‘less invasive treatments’’ that can
only be applied when the affected area
is verifiably destabilized.
Response: Repair and replacement of
existing culverts damaged or lost due to
a natural disaster is necessary to prevent
excessive soil erosion and damage to
resources and property in unstable
environments. According to the DOI CX
data analyzed, no unanticipated
individual or cumulatively significant
impacts occur when culverts are
repaired or replaced in accordance with
the criteria established in the new
Emergency Stabilization CX 11.9I(1).
The activities and the effects of those
activities covered under this Emergency
Stabilization CX are the same as the DOI
CX and will result in no individually or
cumulatively significant impacts.
Comment: Some comments
recommend that the Emergency
Stabilization CX 11.9I(1) be expanded to
include ‘‘minor herbicide applications.’’
Response: The data analyzed in the
development of the Emergency
Stabilization CX 11.9I(1) excluded the
use of herbicides as a variable in the
analysis. Therefore, the CX 11.9I(1)
explicitly precludes its use with respect
to the application of herbicides.
Responses to Specific Comments on
Section 11.9—Categorical Exclusions
J. Other (sub-part J(12))
J(12)—Comments.
Comment: Some comments ask why
the existing CX 11.9H(12) is being
deleted.
Response: The proposed 516 DM 11
mistakenly left the existing 11.9H(12)
out of the Federal Register (71 FR 4159–
4167, January 25, 2006). This existing
CX is added back into the text of this
Federal Register notice with no changes
to its language, however the citation
number is changed to J(12) for
continued inclusion in the ‘‘Other’’
Category. The language reads,
‘‘Rendering formal classification of
lands as to their mineral character and
waterpower and water storage values.’’
Procedural Requirements
The following list of procedural
requirements has been assembled and
addressed to contribute to this open
review process. Today’s publication is a
notice of an internal Departmental
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action and not a rulemaking. However,
we have addressed the various
procedural requirements that are
generally applicable to proposed and
final rulemaking to show how they
would affect this notice if it were a
rulemaking.
Regulatory Planning and Review
Under Executive Order 12866 (58 FR
51735, October 4, 1993), it has been
determined that this action is the
implementation of policy and
procedures applicable only to the DOI
and not a significant regulatory action.
These policies and procedures would
not impose a compliance burden on the
general economy.
Administrative Procedure Act
This document is not subject to prior
notice and opportunity to comment
because it is a general statement of
policy and procedure (5 U.S.C.
553(b)(A)). However, notice and
opportunity to comment is required by
the CEQ regulations (40 CFR 1507.3(a)).
Regulatory Flexibility Act
This document is not subject to notice
and comment under the Administrative
Procedure Act, and, therefore, is not
subject to the analytical requirements of
the Regulatory Flexibility Act (5 U.S.C.
601 et seq.). This document provides the
DOI with policy and procedures under
NEPA and does not compel any other
party to conduct any action.
Small Business Regulatory Enforcement
Fairness Act
These policies and procedures do not
comprise a major rule under 5 U.S.C.
804(2), the Small Business Regulatory
Enforcement Fairness Act. The
document will not have an annual effect
on the economy of $100 million or more
and is expected to have no significant
economic impacts. Further, it will not
cause a major increase in costs or prices
for consumers, individual industries,
Federal, State, or local government
agencies, or geographic regions and will
(Page 52596) impose no additional
regulatory restraints in addition to those
already in operation. Finally, the
document does not have significant
adverse effects on competition,
employment, investment, productivity,
innovation, or the ability of United
States-based enterprises to compete
with foreign-based enterprises.
Unfunded Mandates Reform Act
In accordance with the Unfunded
Mandates Reform Act (2 U.S.C. 1501 et
seq.), this document will not
significantly or uniquely affect small
governments. A Small Government
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Agency Plan is not required. The
document does not require any
additional management responsibilities.
Further, this document will not produce
a federal mandate of $100 million or
greater in any year, that is, it is not a
significant regulatory action under the
Unfunded Mandates Reform Act. These
policies and procedures are not
expected to have significant economic
impacts nor will they impose any
unfunded mandates on other Federal,
State, or local government agencies to
carry out specific activities.
1999), aff’d 230 F.3d 947, 954–55 (7th
Cir. 2000).
NEPA, this publication will not cause
such interference.
Essential Fish Habitat
We have analyzed this document in
accordance with Section 305(b) of the
Magnuson-Stevens Fishery
Conservation and Management Act and
determined that issuance of this
document will not affect the essential
fish habitat of federally-managed
species; therefore, an essential fish
habitat consultation on this document is
not required.
Authority: The NEPA, the National
Environmental Quality Improvement Act of
1970, as amended (42 U.S.C. 4371 et seq.);
Executive Order 11514, March 5, 1970, as
amended by Executive Order 11991, May 24,
1977; and CEQ regulations 40 CFR 1507.3.
Federalism
Consultation and Coordination With
Indian Tribal Governments
In accordance with Executive Order
13175 of November 6, 2000, and 512
DM Ch 2, we have assessed this
document’s impact on tribal trust
resources and have determined that it
does not directly affect tribal resources
since it describes the DOI’s procedures
for its compliance with NEPA.
In accordance with Executive Order
13132, this document does not have
significant federalism effects; therefore,
a federalism assessment is not required.
The policies and procedures will not
have substantial direct effects on the
states, on the relationship between the
Federal government and the states, or on
the distribution of power and
responsibilities among the various
levels of government. No intrusion on
state policy or administration is
expected, roles or responsibilities of
federal or state governments will not
change, and fiscal capacity will not be
substantially, directly affected.
Therefore, the document does not have
significant effects on or implications for
federalism.
Paperwork Reduction Act
This document does not require
information collection, as defined under
the Paperwork Reduction Act.
Therefore, this document does not
constitute a new information collection
system requiring Office of Management
and Budget approval under the
Paperwork Reduction Act (44 U.S.C.
3501 et seq.).
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National Environmental Policy Act
The CEQ does not direct agencies to
prepare a NEPA analysis or document
before establishing agency procedures
that supplement the CEQ regulations for
implementing NEPA. Agency NEPA
procedures are procedural guidance to
assist agencies in the fulfillment of
agency responsibilities under NEPA, but
are not the agency’s final determination
of what level of NEPA analysis is
required for a particular proposed
action. The requirements for
establishing agency NEPA procedures
are set forth at 40 CFR 1505.1 and
1507.3. The determination that
establishing NEPA procedures does not
require NEPA analysis and
documentation has been upheld in
Heartwood, Inc. v. U.S. Forest Service,
73 F. Supp. 2d 962, 972–73 (S.D. Ill.
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Actions Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
Executive Order 13211 of May 18,
2001, requires a Statement of Energy
Effects for significant energy actions.
Significant energy actions are actions
normally published in the Federal
Register that lead to the promulgation of
a final rule or regulation and may have
any adverse effects on energy supply,
distribution, or use. We have explained
above that this document is an internal
DM part, which only affects how the
DOI conducts its business under the
NEPA. Revising this manual part does
not constitute rulemaking; therefore, it
is not subject to Executive Order 13211.
Actions to Expedite Energy-Related
Projects
Executive Order 13212 of May 18,
2001, requires agencies to expedite
energy-related projects by streamlining
internal processes while maintaining
safety, public health, and environmental
protections. Today’s publication is in
conformance with this requirement as it
promotes existing process streamlining
requirements and revises the text to
emphasize this concept (see Chapter 4,
subpart 4.16).
Government Actions and Interference
With Constitutionally Protected Property
Rights
In accordance with Executive Order
12630 (March 15, 1988), and Part 318 of
the DM, the DOI has reviewed today’s
notice to determine whether it would
interfere with constitutionally protected
property rights. As internal instructions
to bureaus on the implementation of the
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Willie R. Taylor,
Director, Office of Environmental Policy and
Compliance.
An electronic copy may be obtained
from the Department of the Interior Web
site https://elips.doi.gov.
Department of the Interior
Departmental Manual
llllllllllllllllll
l
Effective Date: llllllllll
Series: Environmental Quality.
Part 516: National Environmental Policy
Act of 1969.
Chapter 11: Managing the NEPA
Process—Bureau of Land
Management.
Originating Office: Office of
Environmental Policy and
Compliance.
llllllllllllllllll
l
516 DM 11
11.1
Purpose
This chapter provides supplementary
requirements for implementing
provisions of 516 DM Chapters 1
through 6 for the Department of the
Interior’s Bureau of Land Management
(BLM). The BLM’s National
Environmental Policy Act (NEPA)
Handbook (H–1790–1) provides
additional guidance.
11.2
NEPA Responsibilities
A. The Director and Deputy
Director(s) are responsible for the BLM
NEPA compliance activities.
B. The Assistant Director, Renewable
Resources and Planning, is responsible
for national NEPA compliance
leadership and coordination, program
direction, policy, and protocols
development, and implementation of
the same at the line management level.
The Division of Planning and Science
Policy, within the Assistant Directorate,
Renewable Resources and Planning, has
the BLM lead for the NEPA compliance
program direction and oversight.
C. The BLM Office Directors and other
Assistant Directors are responsible for
cooperating with the Assistant Director,
Renewable Resources and Planning, to
ensure that the BLM NEPA compliance
procedures operate as prescribed within
their areas of responsibility.
D. The BLM Center Directors are
responsible for cooperating with the
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Assistant Director, Renewable Resources
and Planning, to ensure that the BLM
NEPA compliance procedures operate as
prescribed within their areas of
responsibility.
E. The State Directors are responsible
to the Director/Deputy Director(s) for
overall direction, integration and
implementation of the BLM NEPA
compliance procedures in their states.
This includes managing for the
appropriate level of public notification
and participation, and ensuring
production of quality environmental
review and decision documents. Deputy
State Directors serve as focal points for
NEPA compliance matters at the state
level.
F. The District and Field Managers are
responsible for NEPA compliance at the
local level.
11.3
External Applicants’ Guidance
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A. General
(1) For all external proposals,
applicants should make initial contact
with the Responsible Official (District
Manager, Field Manager, or State
Director) responsible for the affected
public lands as soon as possible after
determining the BLM’s involvement.
This early contact is necessary to allow
the BLM to consult early with
appropriate state and local agencies and
tribes and with interested private
persons and organizations, and to
commence its NEPA process at the
earliest possible time.
(2) When a proposed action has the
potential to affect public lands in more
than one administrative unit, the
applicant may initially contact any
Responsible Official whose jurisdiction
is involved. The BLM may then
designate a lead office to coordinate
between BLM jurisdictions.
(3) Potential applicants may secure
from the Responsible Official a list of
NEPA and other relevant regulations
and requirements for environmental
review related to each applicant’s
proposed action. The purpose of making
these regulations and requirements
known in advance is to assist the
applicant in the development of an
adequate and accurate description of the
proposed action when the applicant
submits their project application. The
list provided to the applicant may not
fully disclose all relevant regulations
and requirements because additional
requirements could be identified after
review of the applicant’s proposal
document(s) and as a result of the
‘‘scoping’’ process.
(4) The applicant is encouraged to
advise the BLM of their intentions early
on in their planning process. Early
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communication is necessary so that the
BLM can efficiently advise the applicant
on the anticipated type of NEPA review
required, information needed, and
potential data gaps that may or may not
need to be filled, so that the BLM can
describe the relevant regulations and
requirements likely to affect the
proposed action(s), and to discuss
scheduling expectations.
B. Regulations: The following list of
potentially relevant regulations should
be considered at a minimum. Many
other regulations affect public lands—
some of which are specific to the BLM,
while others are applicable across a
broad range of federal programs (e.g.,
Protection of Historic and Cultural
Programs—36 Code of Federal
Regulations (CFR) Part 800).
(1) Resource Management Planning—
43 CFR 1610;
(2) Withdrawals—43 CFR 2300;
(3) Land Classification—43 CFR 2400;
(4) Disposition: Occupancy and Use—
43 CFR 2500;
(5) Disposition: Grants—43 CFR 2600;
(6) Disposition: Sales—43 CFR 2700;
(7) Use: Rights-of-Way—43 CFR 2800;
(8) Use: Leases and Permits—43 CFR
2900;
(9) Oil and Gas Leasing—43 CFR
3100;
(10) Geothermal Resources Leasing—
43 CFR 3200;
(11) Coal Management—43 CFR 3400;
(12) Leasing of Solid Minerals Other
than Coal/Oil Shale—43 CFR 3500;
(13) Mineral Materials Disposal—43
CFR 3600;
(14) Mining Claims Under the General
Mining Laws—43 CFR 3800;
(15) Grazing Administration—43 CFR
4100;
(16) Wild Free-Roaming Horse and
Burro Management—43 CFR 4700;
(17) Forest Management—43 CFR
5000;
(18) Wildlife Management—43 CFR
6000;
(19) Recreation Management—43 CFR
8300; and
(20) Wilderness Management—43
CFR 6300.
11.4
General Requirements
The Council on Environmental
Quality (CEQ) regulations state that
federal agencies shall reduce paperwork
and delay (40 CFR 1500.4 and 1500.5)
to the fullest extent possible. The
information used in any NEPA analysis
must be of high quality. Accurate
scientific analysis, agency expert
comments, and public scrutiny are
essential to implementing the NEPA (40
CFR 1500.1(b)). Environmental
documents should be concise and
written in plain language (40 CFR
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1502.8), so they can be understood and
should concentrate on the issues that
are truly significant to the action in
question rather than amassing needless
detail (40 CFR 1500.1(b)).
A. Reduce paperwork and delays: The
Responsible Official will avoid
unnecessary duplication of effort and
promote cooperation with other federal
agencies that have permitting, funding,
approving, or other consulting or
coordinating requirements associated
with the proposed action. The
Responsible Official shall, as
appropriate, integrate NEPA
requirements with other environmental
review and consultation requirements
(40 CFR 1500.4(k)); tier to broader
environmental review documents (40
CFR 1502.20); incorporate by reference
relevant studies and analyses (40 CFR
1502.21); adopt other agency
environmental analyses (40 CFR
1506.3); and supplement analyses with
new information (40 CFR 1502.9).
B. Eliminate duplicate tribal, state,
and local governmental procedures (40
CFR 1506.2): The Responsible Official
will cooperate with other governmental
entities to the fullest extent possible to
reduce duplication between federal,
state, local and tribal requirements in
addition to, but not in conflict with,
those in the NEPA. Cooperation may
include the following: common
databases; joint planning processes;
joint science investigations; joint public
meetings and hearings; and joint
environmental assessment (EA) level
and joint environmental impact
statement (EIS) level analyses using
joint lead or cooperating agency status.
C. Consult and coordinate: The
Responsible Official will determine
early in the process the appropriate type
and level of consultation and
coordination required with other federal
agencies and with state, local and tribal
governments. After the NEPA review is
completed, coordination will often
continue throughout project
implementation, monitoring, and
evaluation.
D. Involve the public: The public must
be involved early and continuously, as
appropriate, throughout the NEPA
process. The Responsible Official shall
ensure that:
(1) The type and level of public
involvement shall be commensurate
with the NEPA analysis needed to make
the decision.
(2) When feasible, communities can
be involved through consensus-based
management activities. Consensus-based
management includes direct community
involvement in the BLM activities
subject to NEPA analyses, from initial
scoping to implementation and
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monitoring of the impacts of the
decision. Consensus-based management
seeks to achieve agreement from diverse
interests on the goals, purposes, and
needs of the BLM plans and activities
and the methods needed to achieve
those ends. The BLM retains exclusive
decision-making responsibility and
shall exercise that responsibility in a
timely manner.
E. Implement Adaptive Management:
The Responsible Official is encouraged
to build ‘‘Adaptive Management’’
practice in to their proposed actions and
NEPA compliance activities and train
personnel in this important
environmental concept.
Adaptive Management in the DOI is a
system of management practices based
on clearly identified outcomes,
monitoring to determine if management
actions are meeting outcomes, and the
facilitation of management changes to
ensure that outcomes are met, or
reevaluated as necessary. Such
reevaluation may require new or
supplemental NEPA compliance.
Adaptive Management recognizes that
knowledge about natural resource
systems is sometimes uncertain and is
the preferred method for addressing
these cases. The preferred alternative
should include sufficient flexibility to
allow for adjustments in
implementation in response to
monitoring results.
F. Train for public and community
involvement: The BLM employee(s) that
facilitate(s) public and community
involvement in the NEPA process
should have training in public
involvement, alternative dispute
resolution, negotiation, meeting
facilitation, collaboration, and/or
partnering.
G. Limitations on Actions during the
NEPA process: The following guidance
may aid in fulfilling the requirements of
40 CFR 1506.1. During the preparation
of a program or plan NEPA document,
the Responsible Official may undertake
any major Federal action within the
scope and analyzed in the existing
NEPA document supporting the current
plan or program, so long as there is
adequate NEPA documentation to
support the individual action.
11.5 Plan Conformance
Where a BLM land use plan (LUP)
exists, a proposed action must be in
conformance with the plan. This means
that the proposed action must be
specifically provided for in the plan, or
if not specifically mentioned, the
proposal must be clearly consistent with
the terms, conditions, and decisions of
the plan or plan as amended. If it is
determined that the proposed action
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does not conform to the plan, the
Responsible Official may:
(A) Reject the proposal,
(B) Modify the proposal to conform to
the land use plan, or
(C) Complete appropriate plan
amendments and associated NEPA
compliance requirements prior to
proceeding with the proposed action.
11.6 Existing Documentation
(Determination of NEPA Adequacy)
The Responsible Official may
consider using existing NEPA analysis
for a proposed action when the record
documents show that the following
conditions are met.
(A) The proposed action is adequately
covered by (i.e., is within the scope of
and analyzed in) relevant existing
analyses, data, and records; and
(B) There are no new circumstances,
new information, or unanticipated or
unanalyzed environmental impacts that
warrant new or supplemental analysis.
If the Responsible Official determines
that existing NEPA documents
adequately analyzed the effects of the
proposed action, this determination,
usually prepared in a Determination of
NEPA Adequacy (DNA) worksheet to
provide the administrative record
support, serves as an interim step in the
BLM’s internal decision-making
process. The DNA is intended to
evaluate the coverage of existing
documents and the significance of new
information, but does not itself provide
NEPA analysis. If the Responsible
Official concludes that the proposed
action(s) warrant additional review,
information from the DNA worksheet
may be used to facilitate the preparation
of the appropriate level of NEPA
analysis.
The BLM’s NEPA Handbook and
program specific regulations and
guidance describe additional steps
needed to make and document the
agency’s final determination regarding a
proposed action.
11.7 Actions Requiring an
Environmental Assessment (EA)
A. An EA is a concise public
document that serves to:
(1) Provide sufficient evidence and
analysis for determining whether to
prepare an environmental impact
statement (EIS) or a Finding of No
Significant Impact (FONSI);
(2) Aid the BLM’s compliance with
NEPA when an EIS is not necessary; and
(3) Facilitate preparation of an EIS
when one is necessary.
B. Unlike an EIS that requires much
more, an EA must include the following
four items identified in 40 CFR
1508.9(b):
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(1) The need for the proposal.
(2) Alternatives as described in
Section 102(2)(E) of NEPA.
(3) The environmental impacts of the
proposed action and alternatives.
(4) A listing of agencies and persons
consulted.
C. An EA is usually the appropriate
NEPA document for:
(1) Land Use Plan Amendments;
(2) Land use plan implementation
decisions, including but not limited to
analysis for implementation plans such
as watershed plans or coordinated
resource activity plans, resource use
permits (except for those that are
categorically excludable), and sitespecific project plans, such as
construction of a trail.
D. An EA should be completed when
the Responsible Official is uncertain of
the potential for significant impacts and
needs further analysis to make the
determination.
E. If, for any of these actions, it is
anticipated or determined that an EA is
not appropriate because of potential
significant impacts, an EIS will be
prepared.
11.8 Major Actions Requiring an EIS
A. An EIS level analysis should be
completed when an action meets either
of the two following criteria.
(1) If the impacts of a proposed action
are expected to be significant; or
(2) In circumstances where a
proposed action is directly related to
another action(s), and cumulatively the
effects of the actions taken together
would be significant, even if the effects
of the actions taken separately would
not be significant,
B. The following types of BLM actions
will normally require the preparation of
an EIS:
(1) Approval of Resource Management
Plans.
(2) Proposals for Wild and Scenic
Rivers and National Scenic and Historic
Trails.
(3) Approval of regional coal lease
sales in a coal production region.
(4) Decisions to issue a coal
preference right lease.
(5) Approval of applications to the
BLM for major actions in the following
categories:
(a) Sites for steam-electric
powerplants, petroleum refineries,
synfuel plants, and industrial facilities;
and
(b) Rights-of-way for major reservoirs,
canals, pipelines, transmission lines,
highways, and railroads.
(6) Approval of operations that would
result in liberation of radioactive tracer
materials or nuclear stimulation.
(7) Approval of any mining operations
where the area to be mined, including
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any area of disturbance, over the life of
the mining plan, is 640 acres or larger
in size.
C. If potentially significant impacts
are not anticipated for these actions, an
EA will be prepared.
11.9 Actions Eligible for a Categorical
Exclusion (CX)
The Departmental Manual (516 DM
2.3A(3) and appendix 2) requires that
before any action described in the
following list of CXs is used, the list of
‘‘extraordinary circumstances’’ must be
reviewed for applicability. If a CX does
not pass the ‘‘extraordinary
circumstances’’ test, the proposed action
analysis defaults to either an EA or an
EIS. When no ‘‘extraordinary
circumstances’’ apply, the following
activities do not require the preparation
of an EA or EIS. In addition, see 516 DM
2, appendix 1 for a list of DOI-wide
categorical exclusions. As proposed
actions are designed and then reviewed
against the CX list, proposed actions or
activities must be, at a minimum,
consistent with the DOI and the BLM
regulations, manuals, handbooks,
policies, and applicable land use plans
regarding design features, best
management practices, terms and
conditions, conditions of approval, and
stipulations.
A. Fish and Wildlife
(1) Modification of existing fences to
provide improved wildlife ingress and
egress.
(2) Minor modification of water
developments to improve or facilitate
wildlife use (e.g., modify enclosure
fence, install flood valve, or reduce
ramp access angle).
(3) Construction of perches, nesting
platforms, islands, and similar
structures for wildlife use.
(4) Temporary emergency feeding of
wildlife during periods of extreme
adverse weather conditions.
(5) Routine augmentations, such as
fish stocking, providing no new species
are introduced.
(6) Relocation of nuisance or
depredating wildlife, providing the
relocation does not introduce new
species into the ecosystem.
(7) Installation of devices on existing
facilities to protect animal life, such as
raptor electrocution prevention devices.
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B. Oil, Gas, and Geothermal Energy
(1) Issuance of future interest leases
under the Mineral Leasing Act for
Acquired Lands, where the subject
lands are already in production.
(2) Approval of mineral lease
adjustments and transfers, including
assignments and subleases.
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(3) Approval of unitization
agreements, communitization
agreements, drainage agreements,
underground storage agreements,
development contracts, or geothermal
unit or participating area agreements.
(4) Approval of suspensions of
operations, force majeure suspensions,
and suspensions of operations and
production.
(5) Approval of royalty
determinations, such as royalty rate
reductions.
(6) Approval of Notices of Intent to
conduct geophysical exploration of oil,
gas, or geothermal, pursuant to 43 CFR
3150 or 3250, when no temporary or
new road construction is proposed.
C. Forestry
(1) Land cultivation and silvicultural
activities (excluding herbicide
application) in forest tree nurseries,
seed orchards, and progeny test sites.
(2) Sale and removal of individual
trees or small groups of trees which are
dead, diseased, injured, or which
constitute a safety hazard, and where
access for the removal requires no more
than maintenance to existing roads.
(3) Seeding or reforestation of timber
sales or burn areas where no chaining is
done, no pesticides are used, and there
is no conversion of timber type or
conversion of non-forest to forest land.
Specific reforestation activities covered
include: seeding and seedling plantings,
shading, tubing (browse protection),
paper mulching, bud caps, ravel
protection, application of non-toxic big
game repellant, spot scalping, rodent
trapping, fertilization of seed trees,
fence construction around out-planting
sites, and collection of pollen, scions
and cones.
(4) Pre-commercial thinning and
brush control using small mechanical
devices.
(5) Disposal of small amounts of
miscellaneous vegetation products
outside established harvest areas, such
as Christmas trees, wildings, floral
products (ferns, boughs, etc.), cones,
seeds, and personal use firewood.
(6) Felling, bucking, and scaling
sample trees to ensure accuracy of
timber cruises. Such activities:
(a) Shall be limited to an average of
one tree per acre or less,
(b) Shall be limited to gas-powered
chainsaws or hand tools,
(c) Shall not involve any road or trail
construction,
(d) Shall not include the use of
ground based equipment or other
manner of timber yarding, and
(e) Shall be limited to the Coos Bay,
Eugene, Medford, Roseburg, and Salem
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45539
Districts and Lakeview District—
Klamath Falls Resource Area in Oregon.
(7) Harvesting live trees not to exceed
70 acres, requiring no more than 0.5
mile of temporary road construction.
Such activities:
(a) Shall not include even-aged
regeneration harvests or vegetation type
conversions.
(b) May include incidental removal of
trees for landings, skid trails, and road
clearing.
(c) May include temporary roads
which are defined as roads authorized
by contract, permit, lease, other written
authorization, or emergency operation
not intended to be part of the BLM
transportation system and not necessary
for long-term resource management.
Temporary roads shall be designed to
standards appropriate for the intended
uses, considering safety, cost of
transportation, and impacts on land and
resources; and
(d) Shall require the treatment of
temporary roads constructed or used so
as to permit the reestablishment by
artificial or natural means, or vegetative
cover on the roadway and areas where
the vegetative cover was disturbed by
the construction or use of the road, as
necessary to minimize erosion from the
disturbed area. Such treatment shall be
designed to reestablish vegetative cover
as soon as practicable, but at least
within 10 years after the termination of
the contract.
Examples include, but are not limited
to:
(a) Removing individual trees for
sawlogs, specialty products, or
fuelwood.
(b) Commercial thinning of
overstocked stands to achieve the
desired stocking level to increase health
and vigor.
(8) Salvaging dead or dying trees not
to exceed 250 acres, requiring no more
than 0.5 mile of temporary road
construction. Such activities:
(a) May include incidental removal of
live or dead trees for landings, skid
trails, and road clearing.
(b) May include temporary roads
which are defined as roads authorized
by contract, permit, lease, other written
authorization, or emergency operation
not intended to be part of the BLM
transportation system and not necessary
for long-term resource management.
Temporary roads shall be designed to
standards appropriate for the intended
uses, considering safety, cost of
transportation, and impacts on land and
resources; and
(c) Shall require the treatment of
temporary roads constructed or used so
as to permit the reestablishment, by
artificial or natural means, of vegetative
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cover on the roadway and areas where
the vegetative cover was disturbed by
the construction or use of the road, as
necessary to minimize erosion from the
disturbed area. Such treatment shall be
designed to reestablish vegetative cover
as soon as practicable, but at least
within 10 years after the termination of
the contract.
(d) For this CX, a dying tree is defined
as a standing tree that has been severely
damaged by forces such as fire, wind,
ice, insects, or disease, and that in the
judgment of an experienced forest
professional or someone technically
trained for the work, is likely to die
within a few years.
Examples include, but are not limited
to:
(a) Harvesting a portion of a stand
damaged by a wind or ice event.
(b) Harvesting fire damaged trees.
(9) Commercial and non-commercial
sanitation harvest of trees to control
insects or disease not to exceed 250
acres, requiring no more than 0.5 miles
of temporary road construction. Such
activities:
(a) May include removal of infested/
infected trees and adjacent live
uninfested/uninfected trees as
determined necessary to control the
spread of insects or disease; and
(b) May include incidental removal of
live or dead trees for landings, skid
trails, and road clearing.
(c) May include temporary roads
which are defined as roads authorized
by contract, permit, lease, other written
authorization, or emergency operation
not intended to be part of the BLM
transportation system and not necessary
for long-term resource management.
Temporary roads shall be designed to
standards appropriate for the intended
uses, considering safety, cost of
transportation, and impacts on land and
resources; and
(d) Shall require the treatment of
temporary roads constructed or used so
as to permit the reestablishment, by
artificial or natural means, of vegetative
cover on the roadway and areas where
the vegetative cover was disturbed by
the construction or use of the road, as
necessary to minimize erosion from the
disturbed area. Such treatment shall be
designed to reestablish vegetative cover
as soon as practicable, but at least
within 10 years after the termination of
the contract.
Examples include, but are not limited
to:
(a) Felling and harvesting trees
infested with mountain pine beetles and
immediately adjacent uninfested trees to
control expanding spot infestations; and
(b) Removing or destroying trees
infested or infected with a new exotic
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16:39 Aug 13, 2007
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insect or disease, such as emerald ash
borer, Asian longhorned beetle, or
sudden oak death pathogen.
D. Rangeland Management
(1) Approval of transfers of grazing
preference.
(2) Placement and use of temporary
(not to exceed one month) portable
corrals and water troughs, providing no
new road construction is needed.
(3) Temporary emergency feeding of
livestock or wild horses and burros
during periods of extreme adverse
weather conditions.
(4) Removal of wild horses or burros
from private lands at the request of the
landowner.
(5) Processing (transporting, sorting,
providing veterinary care, vaccinating,
testing for communicable diseases,
training, gelding, marketing,
maintaining, feeding, and trimming of
hooves of) excess wild horses and
burros.
(6) Approval of the adoption of
healthy, excess wild horses and burros.
(7) Actions required to ensure
compliance with the terms of Private
Maintenance and Care agreements.
(8) Issuance of title to adopted wild
horses and burros.
(9) Destroying old, sick, and lame
wild horses and burros as an act of
mercy.
(10) Vegetation management
activities, such as seeding, planting,
invasive plant removal, installation of
erosion control devices (e.g., mats/
straw/chips), and mechanical
treatments, such as crushing, piling,
thinning, pruning, cutting, chipping,
mulching, mowing, and prescribed fire
when the activity is necessary for the
management of vegetation on public
lands. Such activities:
(a) Shall not exceed 4,500 acres per
prescribed fire project and 1,000 acres
for other vegetation management
projects;
(b) Shall not be conducted in
Wilderness areas or Wilderness Study
Areas;
(c) Shall not include the use of
herbicides, pesticides, biological
treatments or the construction of new
permanent roads or other new
permanent infrastructure;
(d) May include temporary roads
which are defined as roads authorized
by contract, permit, lease, other written
authorization, or emergency operation
not intended to be part of the BLM
transportation system and not necessary
for long-term resource management.
Temporary roads shall be designed to
standards appropriate for the intended
uses, considering safety, cost of
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transportation, and impacts on land and
resources; and
(e) Shall require the treatment of
temporary roads constructed or used so
as to permit the reestablishment, by
artificial or natural means, of vegetative
cover on the roadway and areas where
the vegetative cover was disturbed by
the construction or use of the road, as
necessary to minimize erosion from the
disturbed area. Such treatment shall be
designed to reestablish vegetative cover
as soon as practicable, but at least
within 10 years after the termination of
the contract.
(11) Issuance of livestock grazing
permits/leases where
(a) The new grazing permit/lease is
consistent with the use specified on the
previous permit/lease, such that
(1) the same kind of livestock is
grazed,
(2) the active use previously
authorized is not exceeded, and
(3) grazing does not occur more than
14 days earlier or later than as specified
on the previous permit/lease, and
(b) The grazing allotment(s) has been
assessed and evaluated and the
Responsible Official has documented in
a determination that the allotment(s) is
(1) meeting land health standards, or
(2) not meeting land health standards
due to factors that do not include
existing livestock grazing.
E. Realty
(1) Withdrawal extensions or
modifications, which only establish a
new time period and entail no changes
in segregative effect or use.
(2) Withdrawal revocations,
terminations, extensions, or
modifications; and classification
terminations or modifications which do
not result in lands being opened or
closed to the general land laws or to the
mining or mineral leasing laws.
(3) Withdrawal revocations,
terminations, extensions, or
modifications; classification
terminations or modifications; or
opening actions where the land would
be opened only to discretionary land
laws and where subsequent
discretionary actions (prior to
implementation) are in conformance
with and are covered by a Resource
Management Plan/EIS (or plan
amendment and EA or EIS).
(4) Administrative conveyances from
the Federal Aviation Administration
(FAA) to the State of Alaska to
accommodate airports on lands
appropriated by the FAA prior to the
enactment of the Alaska Statehood Act.
(5) Actions taken in conveying
mineral interest where there are no
known mineral values in the land under
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Section 209(b) of the Federal Land
Policy and Management Act of 1976
(FLPMA).
(6) Resolution of class one color-oftitle cases.
(7) Issuance of recordable disclaimers
of interest under Section 315 of FLPMA.
(8) Corrections of patents and other
conveyance documents under Section
316 of FLPMA and other applicable
statutes.
(9) Renewals and assignments of
leases, permits, or rights-of-way where
no additional rights are conveyed
beyond those granted by the original
authorizations.
(10) Transfer or conversion of leases,
permits, or rights-of-way from one
agency to another (e.g., conversion of
Forest Service permits to a BLM Title V
Right-of-way).
(11) Conversion of existing right-ofway grants to Title V grants or existing
leases to FLPMA Section 302(b) leases
where no new facilities or other changes
are needed.
(12) Grants of right-of-way wholly
within the boundaries of other
compatibly developed rights-of-way.
(13) Amendments to existing rightsof-way, such as the upgrading of
existing facilities, which entail no
additional disturbances outside the
right-of-way boundary.
(14) Grants of rights-of-way for an
overhead line (no pole or tower on BLM
land) crossing over a corner of public
land.
(15) Transfers of land or interest in
land to or from other bureaus or federal
agencies where current management
will continue and future changes in
management will be subject to the
NEPA process.
(16) Acquisition of easements for an
existing road or issuance of leases,
permits, or rights-of-way for the use of
existing facilities, improvements, or
sites for the same or similar purposes.
(17) Grant of a short rights-of-way for
utility service or terminal access roads
to an individual residence, outbuilding,
or water well.
(18) Temporary placement of a
pipeline above ground.
(19) Issuance of short-term (3 years or
less) rights-of-way or land use
authorizations for such uses as storage
sites, apiary sites, and construction sites
where the proposal includes
rehabilitation to restore the land to its
natural or original condition.
(20) One-time issuance of short-term
(3 years or less) rights-of-way or land
use authorizations which authorize
trespass action where no new use or
construction is allowed, and where the
proposal includes rehabilitation to
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restore the land to its natural or original
condition.
F. Solid Minerals
(1) Issuance of future interest leases
under the Mineral Leasing Act for
Acquired Lands where the subject lands
are already in production.
(2) Approval of mineral lease
readjustments, renewals, and transfers
including assignments and subleases.
(3) Approval of suspensions of
operations, force majeure suspensions,
and suspensions of operations and
production.
(4) Approval of royalty
determinations, such as royalty rate
reductions and operations reporting
procedures.
(5) Determination and designation of
logical mining units.
(6) Findings of completeness
furnished to the Office of Surface
Mining Reclamation and Enforcement
for Resource Recovery and Protection
Plans.
(7) Approval of minor modifications
to or minor variances from activities
described in an approved exploration
plan for leasable, salable, and locatable
minerals (e.g., the approved plan
identifies no new surface disturbance
outside the areas already identified to be
disturbed).
(8) Approval of minor modifications
to or minor variances from activities
described in an approved underground
or surface mine plan for leasable
minerals (e.g., change in mining
sequence or timing).
(9) Digging of exploratory trenches for
mineral materials, except in riparian
areas.
(10) Disposal of mineral materials,
such as sand, stone, gravel, pumice,
pumicite, cinders, and clay, in amounts
not exceeding 50,000 cubic yards or
disturbing more than 5 acres, except in
riparian areas.
G. Transportation
(1) Incorporation of eligible roads and
trails in any transportation plan when
no new construction or upgrading is
needed.
(2) Installation of routine signs,
markers, culverts, ditches, waterbars,
gates, or cattleguards on/or adjacent to
roads and trails identified in any land
use or transportation plan, or eligible for
incorporation in such plan.
(3) Temporary closure of roads and
trails.
(4) Placement of recreational, special
designation, or information signs, visitor
registers, kiosks, and portable sanitation
devices.
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45541
H. Recreation Management
(1) Issuance of Special Recreation
Permits for day use or overnight use up
to 14 consecutive nights; that impacts
no more than 3 staging area acres; and/
or for recreational travel along roads,
trails, or in areas authorized in a land
use plan. This CX cannot be used for
commercial boating permits along Wild
and Scenic Rivers. This CX cannot be
used for the establishment or issuance
of Special Recreation Permits for
‘‘Special Area’’ management (43 CFR
2932.5).
I. Emergency Stabilization
(1) Planned actions in response to
wildfires, floods, weather events,
earthquakes, or landslips that threaten
public health or safety, property, and/or
natural and cultural resources, and that
are necessary to repair or improve lands
unlikely to recover to a managementapproved condition as a result of the
event. Such activities shall be limited
to: repair and installation of essential
erosion control structures; replacement
or repair of existing culverts, roads,
trails, fences, and minor facilities;
construction of protection fences;
planting, seeding, and mulching; and
removal of hazard trees, rocks, soil, and
other mobile debris from, on, or along
roads, trails, campgrounds, and
watercourses. These activities:
(a) Shall be completed within one
year following the event;
(b) Shall not include the use of
herbicides or pesticides;
(c) Shall not include the construction
of new roads or other new permanent
infrastructure;
(d) Shall not exceed 4,200 acres; and
(e) May include temporary roads
which are defined as roads authorized
by contract, permit, lease, other written
authorization, or emergency operation
not intended to be part of the BLM
transportation system and not necessary
for long-term resource management.
Temporary roads shall be designed to
standards appropriate for the intended
uses, considering safety, cost of
transportation, and impacts on land and
resources; and
(f) Shall require the treatment of
temporary roads constructed or used so
as to permit the reestablishment by
artificial or natural means, or vegetative
cover on the roadway and areas where
the vegetative cover was disturbed by
the construction or use of the road, as
necessary to minimize erosion from the
disturbed area. Such treatment shall be
designed to reestablish vegetative cover
as soon as practicable, but at least
within 10 years after the termination of
the contract.
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J. Other
restored to their natural or original
condition within the same work season.
(5) Reserved.
(6) A single trip in a one month
period for data collection or observation
sites.
(7) Construction of snow fences for
safety purposes or to accumulate snow
for small water facilities.
(8) Installation of minor devices to
protect human life (e.g., grates across
mines).
(9) Construction of small protective
enclosures, including those to protect
reservoirs and springs and those to
protect small study areas.
(10) Removal of structures and
materials of no historical value, such as
mstockstill on PROD1PC66 with NOTICES2
(1) Maintaining land use plans in
accordance with 43 CFR 1610.5–4.
(2) Acquisition of existing water
developments (e.g., wells and springs)
on public land.
(3) Conducting preliminary hazardous
materials assessments and site
investigations, site characterization
studies and environmental monitoring.
Included are siting, construction,
installation and/or operation of small
monitoring devices such as wells,
particulate dust counters and automatic
air or water samples.
(4) Use of small sites for temporary
field work camps where the sites will be
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abandoned automobiles, fences, and
buildings, including those built in
trespass and reclamation of the site
when little or no surface disturbance is
involved.
(11) Actions where the BLM has
concurrence or co-approval with
another DOI agency and the action is
categorically excluded for that DOI
agency.
(12) Rendering formal classification of
lands as to their mineral character,
waterpower, and water storage values.
[FR Doc. E7–15746 Filed 8–13–07; 8:45 am]
BILLING CODE 4310–84–P
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Agencies
[Federal Register Volume 72, Number 156 (Tuesday, August 14, 2007)]
[Notices]
[Pages 45504-45542]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E7-15746]
[[Page 45503]]
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Part II
Department of the Interior
-----------------------------------------------------------------------
Bureau of Land Management
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Notice of Final Action To Adopt Revisions to the Bureau of Land
Management's Procedures for Managing the NEPA Process, Chapter 11 of
the Department of the Interior's Manual Part 516; Notice
Federal Register / Vol. 72, No. 156 / Tuesday, August 14, 2007 /
Notices
[[Page 45504]]
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DEPARTMENT OF THE INTERIOR
Bureau of Land Management
[516 DM 11; WO-210-1610 24 1A]
Notice of Final Action To Adopt Revisions to the Bureau of Land
Management's Procedures for Managing the NEPA Process, Chapter 11 of
the Department of the Interior's Manual Part 516
AGENCY: Bureau of Land Management, Interior.
ACTION: Notice of final action.
-----------------------------------------------------------------------
SUMMARY: The Bureau of Land Management (BLM) gives notice of revised
policies and procedures for implementing the National Environmental
Policy Act (NEPA), as amended, Executive Order (E.O.) 11514, as
amended, E.O. 12114, and Council on Environmental Quality (CEQ)
regulations implementing NEPA. These final implementing procedures are
being issued as Chapter 11 of the Department of the Interior's
Departmental Manual Part 516 (516 DM 11) and supersedes previous
implementation guidance. These revisions update the procedures used to
implement NEPA for actions taken in managing public lands. The BLM's
NEPA compliance procedures can be found at the Department of the
Interior (DOI) Electronic Library of Interior Policies (ELIPS) https://
elips.doi.gov.
The following sections in 516 DM 11 (dated 5/27/04) are affected by
this Federal Register notice: Purpose (11.1); NEPA Responsibilities
(11.2); External Applicant's Guidance (11.3); General Requirements
(11.4), Parts A-G; Plan Conformance (11.5); Existing Documentation
(11.6), Parts A-E; Actions Requiring an Environmental Assessment
(11.7), Parts A-E; and Actions Eligible for Categorical Exclusions
(11.9), categories B-D and G-J. New sub-parts have been added to the
Oil, Gas and Geothermal Energy (B), Forestry (C), and Rangeland
Management (D) categories. Two new categories have been added:
Recreation Management (H) and Emergency Stabilization (I).
Transportation category sub-parts G(1), (2), and (3) have been expanded
to include trails.
DATES: Effective Date: The revised 516 DM 11, including changes and
additions to the categorical exclusions (CXs), is effective upon the
date of publication of this notice in the Federal Register.
ADDRESSES: The BLM's revisions to 516 DM 11 can be accessed
electronically via the Internet at https://elips.doi.gov. Hard copies
are available by contacting Peg Sorensen, Division of Planning and
Science Policy, at 202-452-0364.
FOR FURTHER INFORMATION CONTACT: Peg Sorensen, Division of Planning and
Science Policy, at 202-452-0364.
SUPPLEMENTARY INFORMATION: Final revised NEPA procedures for the DOI
were published in the Federal Register (69 FR 10866-10866, March 8,
2004), and (70 FR 32840-32844, June 6, 2005). The DOI bureau and office
specific procedures are published as chapters in Part 516 of the
Departmental Manual. The 516 DM 11 addresses the BLM policy and
procedures to assure compliance with the spirit and intent of NEPA.
A notice of the proposed revisions to the BLM's ``National
Environmental Policy Act Revised Implementing Procedures'' for 516 DM
11 was published in the Federal Register (71 FR 4159-4167, January 25,
2006), with additional information available at https://www.blm.gov/
planning/news.html. A 30-day public comment period followed that
publication. Consideration of the comments received resulted in the
following modifications to the proposed revised implementing
procedures.
11.1. Purpose: No Change.
11.2. NEPA Responsibilities: Edited title to emphasize that there
are multiple responsibilities.
Parts A-E: Edited to improve readability.
Parts B-E: Clarified executive and delegated leadership
responsibilities.
Parts E & F: Moved sub-part E(1) to a new part F.
11.3. External Applicants' Guidance: Edited title to clarify that
this section only applies to external applicants who are proposing an
action. Language was added from the NEPA to clarify text within the
section.
Part A. General, sub-parts A(2)-(4): Edited to improve readability.
Sub-part A(3): Replaced the ``State Director'' with ``the
Responsible Official'' to clarify that the authorized activity is not
limited to State Directors.
Part B. Regulations, preamble: Edited to improve readability.
11.4. General Requirements:
Part A-H: Revised section titles to create parallel structure.
Edited and reorganized all sections to clarify requirements and improve
readability.
Part A: Added ``integrating NEPA requirements with other
environmental review and consultation requirements'' (from the former
part D) to reduce paperwork and delays.
Part B: Addressed the elimination of duplicate tribal, State, and
local government procedures, and the use of common databases and joint
planning processes, meetings, investigations, and NEPA analyses.
Part C: Addressed consultation and coordination requirements.
Part D, sub-parts (1) & (2): Addressed public involvement
requirements. Eliminated the reference to ``consensus-based decision-
making'' and replaced it with ``consensus-based management'' to be
consistent with direction provided by the DOI. Inserted the DOI's
definition of ``consensus-based management'' and expectations regarding
the process.
Part E: Redefined ``adaptive management'' to match the DOI
definition.
Part F: Clarified a training requirement for the BLM employees
facilitating public and community involvement.
Part G: Clarified action limits during environmental review.
11.5 Plan Conformance: Edited to improve readability. Clarified
what the Responsible Official's options are when a proposed action does
not conform to an approved plan.
11.6 Existing Documentation (Determination of NEPA Adequacy):
Edited the title to create a section header that conforms to a
standardized format. This section was rewritten to clarify the BLM's
policy regarding the use of existing documentation. Operational
information on how to conduct a Determination of NEPA Adequacy (DNA)
will be provided in the BLM NEPA Handbook (H-1790-1).
11.7 Actions Requiring an Environmental Assessment (EA):
Part A: Moved part A information to a new part D. Part A now
defines the purpose and need for an EA.
Part B: Inserted a new requirement to consult 40 CFR 1508.9(b)
which outlines ``discussion'' requirements in an EA.
Part C: Edited to clarify and enhance general understanding of when
an EA is appropriate.
Part D: Directs the Responsible Official to consider an EA if there
are uncertain impacts.
Part E: This new part directs the Responsible Official to prepare
an Environmental Impact Statement (EIS) if it is determined that a CX
or an EA is not appropriate. Removed unnecessary text ``processed in
accordance with 40 CFR 1502.''
11.8 Major Actions Requiring an Environmental Impact Statement
(EIS):
Part A(1): Refined the text to clarify criteria used to consider
when determining whether to prepare an EIS level analysis or not.
Removed the following statement: ``or the impact
[[Page 45505]]
analysis of an action is likely to be highly controversial.'' This edit
was made to clarify the criteria the BLM considers when determining
whether an EIS level analysis is needed. Supplementary guidance on how
to determine significance when considering whether to prepare an EIS,
such as when effects should be considered ``highly controversial,''
will be placed in the BLM NEPA Handbook (BLM H-1790-1).
Part B: Dropped the term ``Wilderness'' from the list of actions
typically requiring an EIS. This edit reflects current program policy
that there will no longer be proposals to designate Wilderness Areas
under Section 603 of FLPMA. Supplementary guidance on how to implement
policy regarding preparation of EISs will be placed in the BLM NEPA
Handbook (BLM H-1790-1).
Part C: Removed unnecessary text ``processed in accordance with 40
CFR 1501.4(e)(2).''
11.9 Actions Eligible for a Categorical Exclusion:
Preamble: Replaced ``exceptions'' with ``extraordinary
circumstances'' to reflect a revision to 516 DM 2.3A(3) made by the DOI
in June 2005. Added a statement identifying the DOI-wide CX in 516 DM
2, appendix 1, available for the BLM consideration. The BLM reviewed
supporting data and conclusions of no significant effect for all
proposed CXs based on comments received. Identified below are revisions
to final CX language based on this review. Some additional information
was added to the administrative file based on the review. In addition,
the BLM reviewed the proposed CXs and this final action establishing
the final CXs in light of CEQ's proposed guidance, ``Establishing,
Revising and Using Categorical Exclusions under the National
Environmental Policy Act,'' (71 FR 54816-54820, September 19, 2006).
The BLM believes that the establishment of the new CXs is consistent
with CEQ's proposed guidance. Based on discussions, review, and to
clarify the intent of the BLM, language has been added indicating the
need for all proposed actions and activities to be, at a minimum,
consistent with the DOI and the BLM regulations, manuals, handbooks,
policies, and applicable Land Use Plans (LUP) regarding design
features, Best Management Practices, Terms and Conditions, Conditions
of Approval, and Stipulations.
A. Fish and Wildlife: Fixed a typographical error in sub-category
(2) by replacing ``value'' with ``valve.''
B. Oil, Gas, and Geothermal Energy:
Sub-category (6): Removed text ``including the establishment of
terms and conditions,'' and edited language to more accurately describe
the actions covered.
Sub-category (7): The BLM has decided not to finalize this proposed
CX (CX B(7)) for the category of actions described as, ``approving the
drilling or subsequent operations of a geothermal well within a
developed field for which a LUP and/or an environmental document,
prepared pursuant to NEPA, analyzed such drilling as within the scope
of a reasonably foreseeable future activity.'' When these actions are
within the scope of the previous NEPA document and sufficiently
analyzed therein, and that determination is documented, no further NEPA
analysis is required. In consultation with CEQ, the BLM has decided
that more focused NEPA documents should be prepared at the outset to
support subsequent implementation of the geothermal field development
plan or utilization plan, and that this practice, combined with a DNA,
would provide a more appropriate method for streamlining the
documentation of the evaluation of subsequent infill well proposals
than a new CX.
Sub-category (8): The BLM has decided not to finalize this proposed
CX. In consultation with CEQ, it was determined that the action of
issuing a geothermal site license or operational permit (CX B(8)) is an
administrative/ministerial function subsequent to the approval of a
utilization plan. Approval of a utilization plan involves analysis of
the environmental effects of constructing and operating the planned
facility. The administrative action of issuing the site license and
permit to operate does not result in additional environmental effects.
Therefore, the BLM will eliminate this additional NEPA review, as
unnecessary and redundant.
C. Forestry:
Sub-category (6): Modified the proposed language and format to
eliminate confusion about the sample tree area limitation and
restricted activities. Added Lakeview District, Klamath Falls Resource
Area to the list of locations where this CX may be used. The Resource
Area was mistakenly left out of the proposed limitation and is now
included because the effects are comparable to the others previously
listed in this section.
Sub-categories (7)-(9): Modified the proposed format and syntax.
Text that defines and limits ``temporary road'' building activities was
added to be consistent with the U.S. Forest Service (FS) standards and
regulations. Text that defines and clarifies ``a dying tree'' was added
for purposes of this category of actions.
Sub-category (9): Modified the example (a) by replacing southern
pine beetle with mountain pine beetle to represent a type of beetle
that occurs in western Oregon.
D. Rangeland Management:
The National Research Council published Rangeland Health: New
Methods to Classify, Inventory, and Monitor Rangelands in 1994. The
concepts identified in that publication were incorporated in the BLM's
grazing regulations and the agency used the term ``rangeland health''
in much of their initial policy and guidance related to implementing
those grazing regulations. Although the term ``rangeland health'' was
first introduced in the grazing regulations, the ``rangeland health
standards'' really apply to the condition of the land itself regardless
of the uses that may influence the health of that land. As a result,
the BLM has begun using the term ``land health'' to avoid the
misperception that these concepts only apply to the grazing program.
For this reason, the term ``land health'' is used in the description of
this proposed CX, even though both terms are likely to be found within
this document or in other background material supporting this document.
Use of the term ``land health'' does not represent any substantive
change in the original definition, concept or use of the term
``rangeland health'' and the reader should view these terms as
interchangeable. The proposed rangeland management sub-categories (10)
and (11) are finalized with the following changes:
Sub-category (10): Lettered the bullet statements, so the first
bullet is criteria (a); moved text (bullets two & three) ``shall be
conducted consistent with the BLM and Departmental procedures and
applicable land and resource management plans (RMP);'' from here to the
general CX introduction to reflect that text applies more generally and
not only to this CX. Modified text of bullet four to exclude use of
this CX for otherwise qualifying ``vegetation management activities''
in Wilderness Study Areas and text becomes new criteria (b). Modified
bullet five to become criteria (c) and added text to indicate that the
CX cannot be used for biological treatments. Finally, added text to
define and limit the use of temporary roads as criteria (d) and (e).
Sub-category (11): Moved criteria (a) to (b) and modified the
phrase ``not meeting standards solely due to factors
[[Page 45506]]
other than existing livestock grazing'' to ``not meeting land health
standards due to factors that do not include existing livestock
grazing.'' Changed the text to clarify that the CX requires land health
assessments be completed prior to considering the application of the
CX. Dropped proposed criteria (b) and replaced it with criteria (a)
that limits the leases/permits eligible for the CX to those where the
lease/permit is consistent with the use specified in the previous
lease/permit, there is no change in the type of livestock, the
previously authorized active use is not exceeded, and grazing does not
occur more than 14 days earlier or later than specified on the previous
lease/permit.
Sub-category (12): Dropped the proposed CX based on further review
of supporting data.
E. Realty:
The proposed revision of sub-category (16) was dropped upon further
review.
F. Solid Minerals: No change was proposed or made.
G. Transportation:
Sub-categories (1), (2), and (3): The word ``existing'' which
originally was used in (1) and (2) has been eliminated because it was
potentially confusing, and the words ``and trails'' have been approved
as proposed.
Sub-category (1) and (2): Replaced ``Incorporating'' for
``Placing'' in sub-category (1), and added ``eligible'' to modify the
language to clarify that only roads and trails meeting criteria
developed in a LUP are to be incorporated into the transportation plan,
or be subject to the actions specified in sub-category (2).
H. Recreation Management:
Sub-category (1): The proposed revision of the previous Category
``H. Other'' to ``Recreation Management and sub-category ``H(5)'' to
``H(1)'' was approved as revised. Increased the day and overnight use
threshold to 14 consecutive nights to be consistent with the practice
of Responsible Officials under provisions in Title 43 of the Code of
Federal Regulations (CFR) that allow such officials to set allowable
length of stay applicable to any casual visitor using public lands (See
43 CFR 8365.1-2 ``Occupancy and Use,'' and 43 CFR 8365.1-6
``Supplementary Rules''). This change has also been made to provide
consistency with the typical length of stay for any casual visitor
using public lands (43 CFR 8364). Changed wording from ``contiguous
acres'' to ``staging area acres'' to better define the limits on area
of impact. Replaced ``travel management areas or networks that are
designated in an approved LUP'' with ``recreational travel along roads,
trails, or in areas authorized in a LUP'' because of confusion over
what constitutes a travel management area or network. Text was added to
include a limitation that this CX cannot be used for the establishment
or issuance of Special Recreation Permits (SRP) for ``Special Area''
management (43 CFR 2932.5). The requirement for Special Area SRPs and
the issuance of individual SRPs in ``Special Areas'' must be directed
by specific land use planning decisions and commensurate NEPA analysis.
I. Emergency Stabilization: This new section was adopted as
proposed with the addition of text to define and limit the use of
temporary roads. The section included a requirement to treat temporary
roads for rehabilitation.
Sub-category (1)(e): Moved text ``shall be conducted consistent
with the BLM and the Department procedures, applicable land and RMPs.''
to general CX introduction to reflect that text applies more generally
and not only to this CX. Renumbered numbered criteria based on the
removal of this text.
J. Other: The previous existing sub-part H was moved to sub-part J
and adopted as proposed with one exception. An existing CX was
mistakenly left out of the January 25, 2006, Federal Register notice.
The following existing CX will be placed in sub-part J (12):
``Rendering formal classification of lands as to their mineral
character and waterpower and water storage values.'' There is no change
to the language.
Appendix 11.1: The DNA Worksheet appendix was deleted. Supplemental
guidance regarding the use of Existing Documentation remains in section
11.6.
Comments on the Proposal
The BLM received more than 72,000 ``comments'' during the 30-day
comment period (January 25, 2006, to February 24, 2006). A ``comment''
is a single, whole submission that may take the form of a letter,
postcard, email, or fax. These comments came from private citizens,
elected officials, and groups and individuals representing businesses,
private organizations, and state and federal agencies. All comments
received were considered in preparing this final action notice.
Public comment on the proposed revisions addressed a wide range of
topics. Many comments support one or more of the proposed revisions or
favor broadening the scope of the revision, while many others oppose
one or more of the proposed revisions or recommend more narrowly
limiting the qualifying criteria for a particular CX. Some comments
state that the 30-day comment period provided insufficient time to
review and comment on the BLM's proposed revisions. The BLM received
extensive and varied comments during the 30-day comment period. Based
on this robust response, the BLM determined that it was unnecessary to
extend the public comment period. Some general comments state that the
BLM is using dated and inadequate scientific information to support
management decisions. They recommend that the BLM adopt a specific
process to systematically incorporate the best available science in all
elements of the BLM public lands management. The BLM Science Strategy
(September 2000) discusses the role of science in the BLM management of
the public lands, and articulates a conceptual framework for
integrating science into the BLM decision-making process. Relevant
scientific information is brought to the decision-maker's attention by
members of the interdisciplinary team of professionals, and through
contract and in-house investigations, science sharing forums, and
technical reports. In addition, the public, cooperators and partners
bring scientific information forward during the environmental review
process. Many comments addressed matters beyond the scope of the
proposed revisions to the 516 DM 11. These included requests for the
BLM to add policy statements to the 516 DM 11 pertaining to conformance
with the Clean Air Act, preserving and honoring valid existing rights,
and conducting cost-benefit analyses. Some comments addressed land
management activities that were neither proposed nor analyzed. Some
comments state that grazing is incompatible with good land stewardship.
Other comments suggested that the proposed changes to 516 DM 11
``denied [the public] their constitutional rights'' or would ``cause
unrestricted use'' of public lands. Responses to most out-of-scope
comments are not provided.
Responses to Specific Comments on Sections 11.1-11.8
11.1 Purpose
Comment: Some comments ask how to access 516 DM 11 and the DOI's
Environmental Statement Memoranda (ESM).
Response: The BLM provided the Web site address to access
procedures (516 DM 11) that are being replaced by this Federal Register
notice in the Summary portion of 71 FR 4159-4167, January 25, 2006. The
proposed changes to these procedures were published in full in the same
Federal Register notice and were
[[Page 45507]]
posted on the DOI, ELIPS Web site in the Departmental Manual chapters
at https://elips.doi.gov. The DOI's ESMs can be accessed through the
DOI's Web site at https://www.doi.gov/oepc via the descriptions in the
left-hand column.
11.3 External Applicants' Guidance
Comment: Some comments ask for information to guide applicants
interested in the BLM program regulations.
Response: The purpose of this section is to provide guidance to
external parties making applications to the BLM. The title has been
changed to make this clear. A list of potentially relevant regulations
is located in part B. Additional regulations, policies, directives, and
guidelines that affect BLM programs may be provided when the applicant
contacts a Responsible Official and describes their proposed action(s).
Comment: A concern was expressed about the absence of NEPA
compliance in the ``applicants'' guidance'' section.
Response: The text has been clarified to address NEPA requirements
for private applicants and other non-federal entities as required by 40
CFR 1501.2(d).
11.4 General Requirements
Comment: Some comments state that local, state, and federal
agencies should not be provided ``cooperating agency status'' because
it blurs the lines of NEPA responsibility.
Response: The NEPA regulations specifically provide for and
encourage the use of ``cooperating agencies'' (40 CFR 1501.6). The
participation of other agencies in the BLM's NEPA processes in no way
``blurs'' the BLM's status as the agency responsible for the NEPA
analysis and the associated decision-making affecting public lands.
Comment: Some comments ask the BLM to revise the language regarding
consensus-based decision-making to clarify that only federal managers
have decision-making authority.
Response: The new language in 516 DM 11.4 D(2) has been added to
describe consensus-based management (as per ESM 03-7) and to clarify
that the BLM has exclusive responsibility for decision-making.
Comment: Some comments recommend that more detailed guidance be
placed in 516 DM 11 to promote consistency between the BLM offices
undertaking public involvement.
Response: The recommended detailed guidance will be considered for
placement in the BLM's NEPA Handbook (H-1790-1). The BLM's public
involvement guidance in 516 DM 11 is consistent with policies and
procedures specified in the NEPA, E.O.s 11514 and 12114, and CEQ
regulations. Federal decision-makers have discretion as to how they
enable public involvement because of the broad range and variety of
potential proposed actions and public interests at stake.
Comment: Some comments state that the BLM should revise 516 DM 11
to require public notice about ``decision documents'' and Findings of
No Significant Impacts (FONSIs) statements.
Response: The CEQ regulations implementing the NEPA have specific
public notification requirements. The BLM will consider adding more
specific guidance regarding public notice of a FONSI in the BLM NEPA
Handbook (H-1790-1). Distinct from its obligations under the NEPA, the
BLM is required under other statutes to provide public notification
regarding management decisions. This notification is done in accordance
with program specific regulations and guidance.
Comment: Some comments state that the public's involvement in the
NEPA process should be more limited, while other comments state that
the public should be given more involvement opportunities than they are
currently provided.
Response: The CEQ regulations implementing the NEPA require
agencies to involve the public in the environmental analysis process.
The timing of public involvement for EISs is set by regulation;
however, the timing and manner of the subject involvement for EAs and
CXs is left to the discretion of the Responsible Official. The BLM is
not changing existing public involvement procedures as a part of the
process of revising this 516 DM 11.
Comment: Some comments suggested that the BLM revise 516 DM 11 to
provide further guidance regarding facilitating public involvement
during NEPA review processes.
Response: Because the range of activities the BLM undertakes is so
broad and varied, and because public involvement can take many forms,
specific guidance on facilitating such public involvement is more
appropriate for inclusion in the BLM's NEPA Handbook (H-1790-1). The
NEPA Handbook provides operational guidance on how to implement the BLM
policy regarding public involvement.
Comment: Some comments state that the BLM should revise the
language in section 11.4 to include reference to the Data Quality Act
(Pub. L. 106-554).
Response: Specific reference to the Data Quality Act in 516 DM 11
was not added. The BLM managers are responsible for ensuring compliance
with all applicable laws and regulations including the Data Quality
Act.
Comment: Some comments ask the BLM to prevent excessive data
collection during the NEPA analysis.
Response: The BLM uses best available data or collects new data
appropriate to the level of the NEPA analysis needed to make an
informed decision regarding the proposed action. The provisions
described in 516 DM 11.4(A-C) are intended to aid in this effort,
provided that the data and analysis compiled by other permitting
agencies is complete, available and sufficient to meet the BLM's needs.
Comment: Some comments express concern that direction for limiting
actions during the NEPA analysis process was too narrowly framed and
did not adequately reflect regulatory requirements.
Response: In addition to noting these limits, the BLM revised
section 11.4G to refer readers directly to the CEQ regulation regarding
the limitation on action during the NEPA analysis as provided in 40 CFR
1506.1, and to provide guidance to aid in fulfilling the regulations.
Comment: Some comments point out that the Federal Register notice
failed to use the DOI's most recently adopted definition of adaptive
management (AM).
Response: The BLM revised the AM definition in 516 DM 11.4E to be
consistent with the DOI definition found in 516 DM 4.16.
Comment: Some comments question the use of AM and request more
information about when it should be used. There is concern that AM not
be used as sole mitigation to justify a FONSI.
Response: The BLM does not use AM as a sole mitigation to justify a
FONSI. Section 11.4E states that the Responsible Official is encouraged
to build AM practices into proposed actions and NEPA compliance
activities and train personnel in this important environmental concept.
The DOI is developing additional guidance for bureaus on the use of an
AM approach to management activities.
Comment: Some comments state that using AM violates the NEPA by (1)
allowing the BLM to defer decisions regarding mitigation--and the
impacts that might result if the mitigation fails--without addressing
those decisions in a NEPA document; (2) removing significant agency
decisions about mitigation, and the possible impacts, from public
review and comment; (3) removing significant impacts that may be
detected during the monitoring process from NEPA analysis; and (4)
[[Page 45508]]
relying heavily on monitoring and evaluation, which the BLM is often
unable to support.
Response: (1) Adaptive Management is a planning tool; it does not
relieve the BLM of the responsibility of meeting the requirements of
the NEPA or other laws. The use of AM does not permit the BLM to defer
``decisions on mitigation and impacts if mitigation fails.'' In fact, a
more vigorous monitoring strategy will help determine if mitigation is
working, and if not, it will help speed up the change in management
action or mitigation strategy. Mitigation and impacts will still be
addressed in the NEPA document as will the AM process itself. Adaptive
Management will not be applied to all resource decisions made. (2)
Stakeholder involvement is a critical aspect of AM. New DOI policy
clearly links stakeholder involvement to implementation of AM from plan
development through implementation. Agency decisions on mitigation and
impacts will not be removed from public review and comment and it is
hoped that there will be an increased level of public involvement. (3)
``Significant impacts'' that are detected during monitoring will not be
removed from the NEPA analysis. Rather, any actions taken to address
``significant impacts'' that may arise will themselves be subject to
appropriate NEPA review, including appropriate public involvement. It
is hoped that a more vigorous stakeholder involvement process using AM
will improve the BLM's ability to detect impacts earlier and make the
necessary resource management changes in partnership with stakeholders.
(4) The AM process will only be used when adequate monitoring and
evaluation can be assured. Successful AM is dependent on good
monitoring and evaluation. If the monitoring strategy goes unfulfilled,
the BLM will need to fall back on a more prescriptive approach.
11.5 Plan Conformance
Comment: Some comments requested that 516 DM 11 direct the BLM
offices to reject proposals unless and until their LUPs are updated to
thoroughly address potential environmental consequences.
Response: Section 11.5 clarifies the requirement for conformance
with LUPs, including when a proposal may be rejected.
11.6 Existing Documentation (Determination of NEPA Adequacy)
Comment: Some comments suggest that 516 DM 11 be revised to
prescribe a minimum level of interdisciplinary review for completing a
DNA.
Response: Section 11.6 has been revised to provide policy guidance
on the use of existing documentation. Operational specifics on how to
implement the policy, such as levels of interdisciplinary review, will
be provided in the BLM NEPA Handbook (H-1790-1).
Comment: Some comments state that the BLM DNA Worksheet does not
meet the requirements of NEPA compliance.
Response: In certain situations, the BLM undertakes a DNA process
to review whether a proposed action has already been fully analyzed in
a NEPA document. Where the proposed action has not already been
analyzed or where it has been analyzed, but new circumstances or
information has come to light, appropriate NEPA analysis and
documentation will be prepared. Operational guidance on how to
implement this policy will be provided in the BLM NEPA Handbook (H-
1790-1). The DNA Worksheet in appendix 1 and implementation-specific
guidance proposed in the January 25, 2006 Federal Register notice has
been deleted from 516 DM 11.
Comment: Some comments state that using the DNA Worksheet process
provides the potential to overlook environmental differences from
widely separated projects and to underestimate the cumulative effects
of nearby projects.
Response: In accordance with 40 CFR 1502.9(c), section 11.6D states
that if existing NEPA documentation is inadequate to cover the proposed
action, an appropriate level NEPA analysis document will be prepared.
The BLM NEPA Handbook (H-1790-1) provides guidance regarding
consideration of cumulative impacts when determining whether a DNA can
be used.
11.7 Actions Requiring an EA
Comment: Some comments expressed confusion about the differences
between actions typically requiring an EA and some of the same actions
proposed in the existing and new CXs.
Response: The January 25, 2006, proposal included several editorial
errors in this sub-part. Sub-part 11.7C(1) was revised for the sake of
clarity.
11.8 Major Actions Requiring an EIS
Comment: Some comments requested clarification of the term ``highly
controversial'' with regard to impacts in sub-part 11.8A(1). The
concern centered on whether the term referred to matters of public/
political controversy versus matters of scientific controversy.
Response: This sub-part has been revised to remove the term
``highly controversial'' as criteria for when an EIS is required.
Guidance on how to determine significance, including when effects
should be considered ``highly controversial'' is applied in accordance
with CEQ regulations and requires agencies to consider the degree to
which effects are likely to be controversial when determining whether
to prepare an EIS. The BLM applies the ``highly controversial'' concept
to disagreements about the nature of the effects. Additional
clarification and examples will be provided in the BLM NEPA Handbook
(H-1790-1).
Comment: Some comments express concern that the lists of actions
that typically require an EA or an EIS were prescriptive, rather than
discretionary, and did not allow for any flexibility.
Response: Although 516 DM 11.7C and 11.8A provide lists of actions
generally requiring EAs or EISs respectively, 516 DM 11.7D, 11.7E and
11.8B specify the flexibility or discretion allowed regarding the
actions on these lists, based on potential impact significance.
11.9 Categorical Exclusions
Responses to section 11.9 comments are divided into two blocks.
Comments of a general nature that may or may not apply to more than one
of the proposed CXs are summarized and responded to as ``general
comments.'' Comments specific to a proposed CX are summarized and
responded to in order of category (e.g., B. Oil, Gas and Geothermal; C.
Forestry; D. Rangeland Management; and so forth) as they occur in 516
DM 11.
General Comments on Categorical Exclusions
Comment: Some comments state that the CX revisions are illegal;
could short circuit important safeguards; circumvent existing laws,
E.O., and the BLM policies; violate the BLM's multiple use mission; and
provide insufficient protection despite the application of
``extraordinary circumstances'' (516 DM 2.3(A) and appendix 2).
Response: The BLM disagrees. The CEQ regulations (40 CFR 1508.4 and
1507.3) authorize Federal agencies to establish and apply CXs. The BLM
followed CEQ regulations in proposing additional CXs to reduce
paperwork and delays (40 CFR 1500.4 and 1500.5) and enable the BLM to
concentrate on environmental issues that are associated with proposed
actions that require further analysis in an EA or an EIS. Each of the
categories of actions in the new CXs were subjected to an
administrative review. This review determined whether there is
sufficient supporting
[[Page 45509]]
evidence, (based on past NEPA analyses) and a review of actions to
support the finding that the activity would not cause individually or
cumulatively significant environmental impacts (https://www.blm.gov/
planning/news.html). When the CXs are used for particular proposed
actions, those actions are reviewed to ensure that they do not involve
``extraordinary circumstances'' and are consistent with all applicable
laws for protection of the environment. In addition, proposed actions
or activities must be, at a minimum, consistent with the DOI and the
BLM regulations, manuals, handbooks, policies, and applicable LUPs
regarding design features, best management practices, terms and
conditions, and conditions of approval, and stipulations. These reviews
ensure proper application of the CXs and act as a ``safeguard'' (516 DM
2.3(A) and appendix 2). Finally, some of the information collected to
prepare the CXs was made available for public review and comment
available at https://www.blm.gov/planning/news.html. Additional
information clarifying these reports is now available at the same Web
site. The establishment and use of CXs has been upheld in Heartwood,
Inc. v. U.S. Forest Service, 73 F. Supp. 2d 962, 972-73 (S.D. Ill.
1999), aff'd 230 F.3d 947, 954-55 (7th Cir. 2000).
Comment: Some comments indicate support for the CX revisions and
some comments would like to expand the categories of activities
excluded from further review under NEPA.
Response: The BLM will continue to compile and review evidence to
determine if additional categories of actions should be excluded from
additional NEPA review. The BLM may propose additional CXs in the
future.
Comment: Some comments state that the BLM erroneously assumes that
``the only function of an EA is to determine whether an EIS is
needed.'' Therefore, ``any EA that resulted in a FONSI need never have
been prepared.''
Response: The BLM disagrees. There are three tasks served by
completing an EA as identified at 40 CFR 1508.9(a)(1)-(3). The BLM
analyzed past environmental documents, including EAs and FONSIs and the
underlying activities in establishing the CXs described in this final
action. Categories of actions were considered eligible for CXs when the
EAs, FONSIs, and subsequent review of these actions showed no
individually or cumulatively significant impacts on the environment.
Comment: Some comments state an opinion that the BLM should ban the
use of CXs.
Response: The BLM disagrees. The BLM establishes CXs in compliance
with the CEQ regulations implementing the NEPA, particularly 40 CFR
1508.4 and 1507.3, which require agencies to develop procedures for
establishing CXs for categories of actions that do not normally require
either an EA or an EIS. The appropriate use of CXs also reduces
paperwork and delays (40 CFR 1500.4 and 1500.5), and enables the BLM to
concentrate on issues that are truly significant and merit review in an
EA or EIS, rather than amassing needless detail for actions
demonstrated not to have significant impacts (40 CFR 1500.1(b)).
Comment: Some comments, while recognizing that the ``extraordinary
circumstances'' review is to occur before an action is determined to be
eligible for use of a CX, express concern that the BLM ``often `defers'
special status species and/or cultural resource inventories on the
sites of proposed actions until after the NEPA process and
documentation is complete.'' The comments go on to question the BLM
practice of ``add[ing] stipulations saying that before any actual
ground disturbance occurs it will conduct the required inventories and
avoid any identified resources.''
Response: The BLM must comply with the NEPA, as well as all
applicable environmental and resource protection laws, such as the
National Historic Preservation Act, 16 U.S.C. 470 et seq., and the
Endangered Species Act, 16 U.S.C. 1531 et seq. (ESA), before any action
is taken. Other than the broad mandate of the Federal Land Policy and
Management Act, 43 U.S.C. 1701 et seq., which directs the BLM to
prepare and maintain an inventory of resource values, there are no
required ``inventories.'' Rather, the BLM has discretion as to when and
how to gather information required to comply with these statutes; that
is, sufficient information may come in different forms, including but
not limited to inventories. In terms of applying the CXs, the NEPA
requires that the BLM first determine whether any extraordinary
circumstances exist that would preclude use of a CX. Several of the
extraordinary circumstances that the BLM must consider directly address
resources mentioned in the comments. For example, extraordinary
circumstances prohibiting the use of a CX include instances where an
individual action may ``have significant impacts on such natural
resources and unique geographic characteristics as historic or cultural
resources'' (516 DM 2 appendix 2(2.2)), ``have significant impacts on
properties listed, or eligible for listing, on the National Register of
Historic Places as determined by either the bureau or office'' (516 DM
2, appendix 2(2.7)), or ``limit access to and ceremonial use of Indian
sacred sites on federal lands by Indian religious practitioners or
significantly adversely affect the physical integrity of such sacred
sites'' (516 DM 2, appendix 2(2.11)). This means that the Responsible
Official must have sufficient information regarding ``cultural
resources'' to complete the ``extraordinary circumstances'' review
before a CX can be used to comply with the NEPA.
Comment: Some comments state that the BLM lacks the staff and
funding for appropriate monitoring of categorically excluded
activities. Some comments express concern that by categorically
excluding more activities, there will be insufficient data to analyze
the impacts of these activities. Other comments ask the BLM to assure
the public that impacts from the implementation of categorically
excluded activities be monitored.
Response: An activity that is subject to a CX by definition is an
activity that is within a category of actions that have previously been
found not to have significant impacts, either individually or
cumulatively. That being said, regardless of whether a proposed
activity is reviewed under an EA, EIS or CX, the BLM monitors the
effects of these activities to the extent its budget allows. The BLM's
program management and associated staffing decisions regarding the
monitoring of effects are subject to the appropriations process. (See,
Anti-Deficiency Act, 31 U.S.C. 1341).
Comment: Some comments state that the BLM should increase public
notification of CX decisions made.
Response: The CEQ regulations (40 CFR 1506.6) require public notice
about the completion of NEPA analysis under certain circumstances.
These regulations do not require public notification of the use of a
CX. Some BLM offices currently support Web sites that list the
decisions made in their management area, including the NEPA documents
associated with those decisions (including applying a CX). For example,
see the Utah State Office Environmental Notification Bulletin Board at
https://www.ut.blm.gov/enbb/index.php.
Comment: Some comments state that the BLM should include the CXs
from the Energy Policy Act of 2005 in the 516 DM 11 revisions.
Response: The CXs included in the Energy Policy Act of 2005 are
statutory CXs; therefore, do not need to be listed in 516 DM 11.
[[Page 45510]]
Comment: Some comments ask the BLM to describe how cumulative
impacts of the proposed CX activities would be evaluated. Some comments
suggest that 516 DM 11 be revised to ensure that the cumulative impacts
of projects covered by a CX are analyzed.
Response: An action can only be categorically excluded from further
NEPA analysis when it has been shown that the action fits within a
category of actions that has already been determined not to have a
significant environmental effect on the human environment, individually
or cumulatively (see 40 CFR 1508.4). For all of the categories of
actions for which the CXs were proposed, the analysis of the NEPA
documents prepared for such actions, as well as subsequent evaluations
of the effects of the actions, showed that the actions did not cause
significant effects. Further, when considering whether to use a CX, one
of the ``extraordinary circumstances'' that must be evaluated is
whether the proposed action may ``have a direct relationship to other
actions with individually insignificant but cumulatively significant
environmental effects'' (516 DM 2.3(A)3 and appendix 2 (2.6)). If it
might, then an EA or an EIS must be completed for the action, and a CX
cannot be applied.
Comment: Some comments ask the BLM to evaluate the cumulative
impacts of the proposed CXs, the revisions to the Northwest Forest
Plan's (NWFP) Survey and Management Program and Aquatic Conservation
Strategy; the National Forest Management Act Planning regulations; and
the National Forest Management Act notices, comment, and appeal
regulations.
Response: The new or modified CXs are specific to a revision of the
procedures described in the 516 DM 11 for implementing the NEPA within
the BLM. The determination that establishing CXs does not require NEPA
analysis and documentation has been upheld in Heartwood, Inc. v. U.S.
Forest Service, 73 F. Supp. 2d 962, 972-73 (S.D. Ill. 1999), aff'd 230
F.3d 947, 954-55 (7th Cir. 2000) (holding creation of CXs to be an
establishment of agency procedure for which CEQ regulations do not
require preparation of an EA or EIS). The CXs proposed in January 2006
and finalized here are part of the BLM's effort to update internal NEPA
implementing procedures. A cumulative effects analysis of the
establishment of these CXs, in relation to the NWFP, the National
Forest Management Act Planning regulations, and the National Forest
Management Act is not appropriate in this context. However, in
developing the Forestry CXs, the BLM reviewed past actions and
associated NEPA documents. These NEPA documents included analyses of
cumulative effects, which in relevant instances, included actions taken
by the Forest Service. The BLM's review of these past actions, the NEPA
analyses specific to the actions, and anticipated effects, as well as
the actions' actual effects, allowed the BLM to determine that the
actions had no individual or cumulative significant impacts, and that
development of a CX covering such actions was warranted. The final
determination whether a specific proposed action will have a
significant cumulative effect or not, is completed at the time the
specific proposal is reviewed by considering the applicability of any
extraordinary circumstances.
Comment: Some comments state that the BLM needs to ensure that
implementation of all the CXs will not cumulatively result in jeopardy
to listed endangered species.
Response: The Responsible Official must ensure that no BLM action
will jeopardize a listed species under the ESA. Before a CX can be
used, the Responsible Official must determine that no ``extraordinary
circumstances'' apply. If ``extraordinary circumstances'' (516 DM
2.3(A)3 and appendix 2 (2.8)), which addresses endangered species,
applies, a CX may not be used.
Responses to Specific Comments on Section 11.9--Categorical Exclusions
B. Oil, Gas, and Geothermal Energy (Sub-parts B(6)-(8))
B(6)--Comments.
Comment: Some comments state that the proposed CX 11.9B(6) should
not be implemented because geophysical operations were excluded when
Congress authorized additional energy development-related CXs under the
Energy Policy Act of 2005.
Response: Section 390 of the Energy Policy Act of 2005 does not
provide for a CX for the geophysical activities described in the
proposed CXs. The Act does not preclude the appropriate exercise of
authority to administratively establish CXs in accordance with the
NEPA, the CEQ regulations, and the DOI and the BLM NEPA procedures.
Comment: Some comments state that the proposed CX 11.9B(6) is a
policy change aimed specifically at benefiting the oil and gas industry
and that as such, is a ``scheme'' to make energy exploration companies
more money.
Response: No change to the CX was requested by these comments, no
changes were made in response. The BLM proposed CX 11.9B(6) because CEQ
implementing regulations (40 CFR 1509.4 and 1507.3) allow federal
agencies to identify categories of actions, which normally do not
require either an EA or an EIS. The development of this CX was based on
generally accepted analytical procedures, which included completion of
a census of available data on geophysical exploration. See https://
www.blm.gov/planning/news.html. One benefit to all stakeholders of
adopting new CXs for activities, which have been shown to have no
individually or cumulatively significant effects, is additional federal
resources can be redirected to analyzing and mitigating activities
likely to have significant adverse environmental consequences.
Comment: Some comments suggest that the proposed CX 11.9B(6) would
promote the segmentation of a major project into several categorically
excluded small projects, which would prevent appropriate consideration
of cumulative impacts.
Response: The BLM disagrees. Geophysical exploration activities are
independent actions and not connected actions as defined in NEPA (40
CFR 1508.25 (a)(1)). Geophysical exploration activities are data
collection activities used to gather information that may be used to
inform future decision-making regarding oil, gas or geothermal
development proposals by providing information on the location of
energy resources. It is not a forgone conclusion that the energy
resources identified through this data collection will actually be
developed. Before a CX can be used, a proposed action must be reviewed
to determine whether or not any of the ``extraordinary circumstance''
(516 DM 2.3(A)3 and appendix 2), applies. In particular,
``extraordinary circumstance'' 2.6 addresses the potential for
significant cumulative impacts; if it does apply, the CX cannot be
used.
Comment: Some comments state that federal court and administrative
decisions have either remanded the BLM decisions to approve geophysical
exploration or affirmed agency decisions, only after the BLM proposed
additional mitigation measures.
Response: The data analyzed and reviewed by the BLM validate the
assertion that the impacts from geophysical operations would not be
significant. Specific to the comment related to litigation, the data
indicate that out of 244 projects reviewed, the NEPA analyses of eight
geophysical exploration projects, supported by EAs, were challenged
through administrative appeals or litigation. Only two of the eight
were remanded to the BLM. In one
[[Page 45511]]
situation, the NEPA document was found inadequate where the BLM failed
to consider reasonable alternatives (such as limiting use to existing
roads) that had been suggested, and in the other, the BLM failed to
provide a comment period that had been promised and that the court
found to be appropriate under the circumstances of that case. Neither
was due to a finding of significant impacts associated with geophysical
exploration. Geophysical exploration (the impacts from those activities
and how the BLM field personnel address the approval process) has
changed over the last several years. There have been lessons learned
from the results of this litigation, from personal observation by field
staff associated with the projects, field data collection through
monitoring, and systematic evaluation of information received from the
proponents. Accumulation of professional knowledge resulted in design
features that previously were not part of proponent geophysical
proposals, yet are now considered routine. Proponents either with or
without the BLM consultation now incorporate best management practices
into proposals. Project design features are site specific to the local
concerns and resource values. They represent a commonality of best
management practices that are integral to the project being authorized.
Field personnel that routinely permit these actions know the needs
based on accumulated professional knowledge of resource concerns in the
area at issue, and either assure these aspects appear in the
proponent's proposal or include them as conditions of approval in the
authorization. ``Conditions of approval'' or ``terms and conditions''
are terms of art that represent the practices and standards that are
routinely applied to geophysical projects specific for that particular
office. Their application does not require a new analysis each time a
project is submitted, but results in a list of measures that the
proponent must implement based on local conditions. In all cases,
proposed actions or activities must be, at a minimum, consistent with
the DOI and the BLM regulations, manuals, handbooks, policies, and
applicable LUPs regarding design features, best management practices,
terms and conditions, conditions of approval, and stipulations. Also
associated with this improved professional knowledge base, of the BLM
field experience, has been the steady improvement of geophysical
techniques and best management practices by the geophysical industry.
Low impact techniques have allowed for substantial reductions in the
amount of actual surface disturbance and associated resource impacts.
Physical impacts such as road construction are rare and the impacts to
soil or vegetation resources are minimal or short-term.
Comment: Some comments state that geophysical exploration
activities cause ``disturbance'' and related erosion impacts, such as
landslides and slumps. Therefore, they recommend that the CX not be
adopted.
Response: Available data supports adoption of the CX. The CX
11.9B(6) was established after careful review of 244 geophysical
exploration projects previously approved by the BLM. The data examined
for these projects included project-specific information on the
location, the type of NEPA review performed, predicted environmental
impacts of proposed actions, and actual environmental impacts after the
action was completed. No projects were shown to have significant
impacts, individually or cumulatively. According to the review of the
NEPA analysis completed for these 244 geophysical exploration projects,
including review of the effects of the completed projects themselves,
predicted significant impacts, including erosion-related impacts as a
result of geophysical exploration, did not occur. In addition, with
respect to the resources mentioned in the comments, the BLM applies
specific ``Terms and Conditions''--as indicated in number seven of the
BLM Form 3150-4 and requires suspension of operations when unnecessary
disturbance to soils may occur. This term and condition is a part of
all geophysical Notices of Intent (see the BLM Form 3150-4). In
addition, if the required ``extraordinary circumstances'' review
conducted for any proposed action indicated such impacts as
``landslides'' and ``slumps'' might be significant, the CX would not be
used.
Comment: Some comments state that the use of the geophysical
exploration CX would have negative impacts on non-commercial uses, such
as scientific, educational, recreational, aesthetic, and spiritual
purposes.
Response: See response above. The BLM reviewed 244 geophysical
exploration projects. None of the projects reviewed during the
establishment of this CX resulted in a significant impact, either
individually or cumulatively. In addition, the BLM will review all
future projects against the DOI's ``extraordinary circumstances.'' If
the review indicates that the action may have a direct relationship to
other actions with individually insignificant, but cumulatively
significant environmental effects (i.e., to non-commercial uses, such
as scientific, educational, recreational, aesthetic and spiritual
purposes), the CX cannot be used.
Comment: Some comments state that geophysical (e.g. seismic)
exploration activities have potentially significant impacts to
environmental and cultural resources.
Response: None of the 244 geophysical exploration projects reviewed
during the establishment of this CX resulted in a significant impact,
either individually or cumulatively. Further, the BLM believes the
established permitting process ensures that if there are potential
individually or cumulatively significant environmental effects, an EA
or EIS, as appropriate, would be done. Included in the permitting
process is the requirement to review the DOI list of ``extraordinary
circumstances'' (516 DM 2.3A(3) & appendix 2) for every proposed
action. ``Cultural resources'' are specifically provided for in this
list. If the required ``extraordinary circumstances'' review indicated
that significant impacts to environmental or cultural resources might
occur, the CX would not be used.
Further, the use of the CX during the NEPA review process does not
eliminate the need to comply with Section 106 of the National
Historical Preservation Act (Pub. L. 89-665) or the Archeological
Resources Protection Act (Pub. L. 96-95), or any other applicable
resource protection law.
Comment: Some comments express concern that geophysical exploration
activities can damage roadless areas by creating noticeable vehicle
routes, which can attract traffic by ``unauthorized'' off-highway
vehicle drivers.
Response: Historically, older geophysical exploration operations
required the use of some type of road construction. These operations
left travelways that would take time to completely reclaim. In the
interim, these routes would remain visible and may have encouraged off-
highway travel by some members of the public. Best management practices
over time have reduced the visibility of noticeable vehicle tracks
through project design features so that non-authorized use is
discouraged. Further, the proposed CX was specifically limited to
geophysical exploration projects that do not involve road construction.
The BLM reviewed 244 geophysical exploration projects during the
establishment of this CX. None of the projects resulted in a
significant impact, either individually or cumulatively. As an
additional limitation, the BLM has added a
[[Page 45512]]
requirement to this CX that when road construction is involved, the CX
would not be used and additional NEPA review would be completed.
Further, the proposed geophysical exploration activities can only
proceed using this CX where none of the ``extraordinary circumstances''
apply (516 DM 2.3A(3) & appendix 2).
Comment: Some comments state that the proposed CX 11.9B(6) would
``wrongly exclude'' the covered actions from compliance with federal
laws protecting wildlife, such as the ESA.
Response: The use of a CX does not eliminate the need to comply
with Section 7 of the ESA or other federal laws. None of the 244
projects reviewed during the establishment of this CX resulted in a
significant impact, either individually or cumulatively. Further, if
the proposed geophysical exploration activity has the potential to
significantly impact listed threatened or endangered species, or their
critical habitat, ``extraordinary circumstance'' 2.8 (516 DM 2 appendix
2.8) applies, and an EA or EIS, as appropriate, is required.
Comment: Some comments state that weed invasion follows the network
of seismic activities across the landscape, which can result in
irreversible weed invasions that radically alter fire cycles and
endanger wildlife habitat.
Response: None of the 244 projects reviewed during the
establishment of this CX resulted in a significant impact, either
individually or cumulatively. In addition, specific to the resource
commented on, if the proposed geophysical exploration action may
contribute to the introduction, continued existence, or spread of
noxious weeds, ``extraordinary circumstance'' 2.12 (516 DM 2, appendix
2.12) would eliminate the decision-maker's ability to use CX 11.9B(6).
An EA or EIS, as appropriate, would be required.
Comment: Some comments ask the BLM to revise the proposed
geophysical exploration CX 11.9B(6) to prohibit seismic activity during
migratory bird breeding season.
Response: None of the 244 projects reviewed during the
establishment of this CX resulted in a significant impact, either
individually or cumulatively. In addition, the DOI and the BLM use a
NEPA review process that ensures that if any of the ``extraordinary
circumstances,'' as defined in 516 DM 2.3A(3) and appendix 2, apply, a
CX cannot be used. ``Extraordinary circumstance'' 2.2 (516 DM 2
appendix 2) affords protection specifically for migratory birds.
Therefore, if a project design feature intended to provide protection
of migratory bird breeding activities in an area occupied by these
birds were to be refused by the applicant, or if its efficacy has not
been sufficiently assured, an EA or EIS, as appropriate, would be
required. Proposed actions or activities must be, at a minimum, (as is
stated in the preamble to this section) consistent with Laws (such as
the Migratory Bird Treaty Act (Pub. L. 86-732), DOI and BLM
regulations, manuals, handbooks, policies, and applicable LUPs
regarding design features, best management practices, terms and
conditions, conditions of approval, and stipulations.
Comment: Some comments ask the BLM to revise the proposed
geophysical exploration CX 11.9B(6) to ensure that operations do not
result in cumulative impacts.
Response: An activity that is subject to a CX by definition is an
activity that has been found not to have significant impacts,
individually or cumulatively. Geophysical exploration activities that
would be authorized under the CX have been shown not to have
significant impacts, either individually or cumulatively based upon the
BLM administrative review of 244 geophysical exploration projects. The
analysis report is available at the BLM Web site at https://www.blm.gov/
planning/news.html. None of the NEPA documentation for the 244
geophysical exploration projects analyzed in the study during the
establishment of the CX indicates the occurrence of significant
impacts. The BLM also employs a NEPA review process that ensures, if
any of the ``extraordinary circumstances,'' as defined in 516 DM
2.3A(3) and appendix 2, apply, a CX cannot be used. One of these
``extraordinary circumstances'' that precludes the use of a CX
addresses cumulative impacts.
Comment: Some comments state that establishment of terms and
conditions for specific proposed actions depends on the soil, weather,
ground cover, and type of machinery to be used in each case; therefore,
the proposed CX would not adequately account for these site-specific
issues.
Response: The BLM agrees that the design of each proposed action
depends on soil, weather, ground cover, and type of machinery to be
used; however, as proposed actions are designed and then reviewed
against the CX list, such actions or activities must be, at a minimum,
consistent with the DOI and the BLM regulations, manuals, handbooks,
policies, and applicable LUPs regarding design features, best
management practices, terms and conditions, conditions of approval, and
stipulations. The geophysical exploration techniques,