Permits for Incidental Take of Eagles and Eagle Nests, 9920-9965 [2024-02182]
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Federal Register / Vol. 89, No. 29 / Monday, February 12, 2024 / Rules and Regulations
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Parts 13 and 22
[Docket No. FWS–HQ–MB–2020–0023;
FF09M30000–234–FXMB12320900000]
RIN 1018–BE70
Permits for Incidental Take of Eagles
and Eagle Nests
Fish and Wildlife Service,
Interior.
ACTION: Final rule.
AGENCY:
We, the U.S. Fish and
Wildlife Service, are revising the
regulations for the issuance of permits
for eagle incidental take and eagle nest
take. The purpose of these revisions is
to increase the efficiency and
effectiveness of permitting, improve
clarity for the regulated community, and
increase the conservation benefit for
eagles. In addition to continuing to
authorize specific permits, we created
general permits for certain activities
under prescribed conditions, including
general permit options for qualifying
wind-energy generation projects, power
line infrastructure, activities that may
disturb breeding bald eagles, and bald
eagle nest take. We also made
improvements to the specific permit
requirements and process. We also
revised permit fees and clarified
definitions.
SUMMARY:
Effective April 12, 2024.
Information Collection Requirements:
If you wish to comment on the
information collection requirements in
this rule, please note that the Office of
Management and Budget (OMB) is
required to make a decision concerning
the collection of information contained
in this rule between 30 and 60 days after
the date of publication of this rule in the
Federal Register. Therefore, comments
should be submitted to OMB by March
13, 2024.
ADDRESSES:
Document availability: The finding of
no significant impact, final
environmental assessment, and
supplementary information used in
development of this rule, including a
list of references cited, technical
appendices, and public comments
received are available at https://
www.regulations.gov in Docket No.
FWS–HQ–MB–2020–0023. Documents
and additional information can also be
found at: https://www.fws.gov/
regulations/eagle.
Information Collection Requirements:
Written comments and suggestions on
the information collection requirements
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DATES:
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should be submitted within 30 days of
publication of this document to https://
www.reginfo.gov/public/do/PRAMain.
Find this particular information
collection by selecting ‘‘Currently under
Review—Open for Public Comments’’ or
by using the search function. Please
provide a copy of your comments to the
Service Information Collection
Clearance Officer, U.S. Fish and
Wildlife Service, 5275 Leesburg Pike,
MS: PRB (JAO/3W), Falls Church, VA
22041–3803 (mail); or Info_Coll@fws.gov
(email). Please reference OMB Control
Number 1018–0167 in the subject line of
your comments.
FOR FURTHER INFORMATION CONTACT:
Jerome Ford, Assistant Director—
Migratory Birds Program, U.S. Fish and
Wildlife Service, telephone: (703) 358–
2606, email: jerome_ford@fws.gov.
Individuals in the United States who are
deaf, deafblind, hard of hearing, or have
a speech disability may dial 711 (TTY,
TDD, or TeleBraille) to access
telecommunications relay services.
Individuals outside the United States
should use the relay services offered
within their country to make
international calls to the point-ofcontact in the United States.
SUPPLEMENTARY INFORMATION:
Background
The U.S. Fish and Wildlife Service
(Service) is the Federal agency delegated
with the primary responsibility for
managing bald eagles (Haliaeetus
leucocephalus) and golden eagles
(Aquila chrysaetos) under the Bald and
Golden Eagle Protection Act 16 U.S.C.
668–668d; [hereinafter the ‘‘Eagle
Act’’]). The Eagle Act prohibits the take,
possession, and transportation of bald
eagles and golden eagles except
pursuant to Federal regulations. The
Eagle Act authorizes the Secretary of the
Interior to issue regulations to permit
the ‘‘taking’’ of eagles for various
purposes, including when ‘‘necessary
. . . for the protection of other interests
in any particular locality,’’ provided the
taking is compatible with the
preservation of eagles (16 U.S.C. 668a).
Regulations pertaining to eagle permits
are set forth in title 50 of the Code of
Federal Regulations (CFR) at 50 CFR
part 22. These regulations authorize the
take of eagles by an activity: They do
not purport to nor can they authorize
the underlying activity itself.
In 2009, subsequent to the delisting of
the bald eagle from the List of
Endangered and Threatened Wildlife at
50 CFR 17.11, the Service promulgated
regulations (74 FR 46836, Sept. 11, 2009
[hereinafter the ‘‘2009 Eagle Rule’’]) at
50 CFR part 22 that established two new
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permit types for the incidental take of
eagles and eagle nests. Incidental take
means foreseeable take that results from,
but is not the purpose of, an activity.
These regulations were revised in 2016
(81 FR 91494, December 16, 2016
[hereinafter the ‘‘2016 Eagle Rule’’]) to
extend tenure, update the Service’s
Eagle Management Unit (EMU)
boundaries, require preconstruction
monitoring for wind-energy projects,
and to amend the preservation standard.
The 2016 Eagle Rule was supported by
a programmatic environmental impact
statement (PEIS), and the Service’s final
decision was described in a record of
decision, both of which are available at
https://www.regulations.gov in Docket
No. FWS–R9–MB–2011–0094.
On September 14, 2021, the Service
published an advance notice of
proposed rulemaking (ANPR) to inform
the public of changes the Service is
considering that expedite and simplify
the permit process authorizing
incidental take of eagles (86 FR 51094).
The ANPR also advised the public that
the Service may prepare a draft
environmental review pursuant to the
National Environmental Policy Act of
1969, as amended. In the ANPR, we
invited input from Tribes, Federal
agencies, State agencies,
nongovernmental organizations, and the
general public for any pertinent issues
we should address, including
alternatives to our proposed approach
for authorizing eagle incidental take.
The public comment period closed on
October 29, 2021. The Service used
these comments to prepare a proposed
rule and a draft environmental
assessment (DEA) which we released on
September 30, 2022 (87 FR 59598). The
60-day public comment period was
extended to December 29, 2022 (87 FR
72957, November 28, 2022). The DEA
and proposed rule are available in
Docket No. FWS–HQ–MB–2020–0023
(available at https://
www.regulations.gov).
Comments and materials we received,
as well as supporting documentation we
use in preparing the environmental
analysis, are available for public
inspection. For more information on
public comments see the Response to
Public Comments below. The Service
also announces the availability of the
finding of no significant impact (FONSI)
for the Service’s final environmental
assessment (FEA). The FONSI is the
final step in the National Environmental
Policy Act (NEPA) process for this eagle
rulemaking action, which includes
revisions to the regulations governing
permits for incidental take of eagles and
take of eagle nests. The FONSI and FEA
are available in Docket No. FWS–HQ–
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MB–2020–0023 (available at https://
www.regulations.gov).
With this rulemaking, we do not
change the 2016 preservation standard
or PEIS management objectives. The
Eagle Act and existing regulations
require that any authorized take of
eagles be ‘‘compatible with the
preservation’’ of bald and golden eagles
(16 U.S.C. 668a). Under existing
regulations, the preservation standard is
defined as consistent with the goals of
maintaining stable or increasing
breeding populations in all eagle
management units and the persistence
of local populations throughout the
geographic range of each species (50
CFR 22.6).
In 2009, the Service adopted different
management criteria for bald eagles and
golden eagles because of the different
population statuses and growth rates of
each species. We determined this
approach is necessary both to achieve
the preservation standard and to avoid
being unnecessarily restrictive. We do
not alter this approach with this
rulemaking. In this rulemaking, the
Service uses the recently updated
population-size estimates and allowable
take limits for bald eagles (87 FR 5493,
February 1, 2022).
This Rulemaking
Overview
The Service creates a new subpart E
within 50 CFR part 22 for eagle permit
regulations authorizing take that is
necessary for the protection of other
(§ 22.210). We further specify activityspecific eligibility criteria and permit
requirements in four sections based on
activity and type of eagle take:
• incidental take for permitting wind
energy (§ 22.250),
• incidental take for permitting power
lines (§ 22.260),
• disturbance take (§ 22.280), and
• nest take (§ 22.300).
For clarity and consistency, we have
also moved regulatory content on permit
conditions to a new section (§ 22.215)
and content on compensatory mitigation
standards to a new section (§ 22.220).
We have created new definitions to
define ‘‘general permit’’ and ‘‘incidental
take’’ and included clarifying
modifications to the definitions of
‘‘eagle management unit,’’ ‘‘eagle nest,’’
and ‘‘in-use nest’’ (§ 22.6). We have
redesignated related regulations
pertaining to permit requirements for
take of golden eagle nests (moved from
§ 22.75 to § 22.325) and permits for bald
eagle take exempted under the
Endangered Species Act (moved from
§ 22.90 to § 22.400) to a new subpart E,
with only the modification of a
nonsubstantive change to the section
title for § 22.325. Finally, we have
adopted administrative updates to 50
CFR part 13, General Permit Procedures,
to update the text regarding
information-collection requirements and
the table of application fees. These
changes to the designated section
numbers for previous regulations are as
follows:
New sections in
50 CFR part 22,
subpart E
Previous regulations in 50 CFR
part 22
Regulatory subject matter
§§ 22.80 and 22.85 ......................
Specific permits ...................................................................................................................
General permits ...................................................................................................................
Permit conditions .................................................................................................................
Compensatory mitigation .....................................................................................................
Wind energy project incidental take ....................................................................................
Power line incidental take ...................................................................................................
Eagle disturbance take ........................................................................................................
Eagle nest take ...................................................................................................................
Golden eagle nest take for resource recovery operations .................................................
Bald eagle take exempted under the Endangered Species Act .........................................
§§ 22.80 and 22.85 ......................
§ 22.80 .........................................
§ 22.80 .........................................
§ 22.80 .........................................
§ 22.80 .........................................
§ 22.85 .........................................
§ 22.75 .........................................
§ 22.90 .........................................
Specific Permits and General Permits for
Eagle Take
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interests in any particular locality (eagle
take for other interests). This new
subpart includes revised provisions for
processing specific permits and creates
general permits. General permits
authorize incidental take by activity
type that occur frequently enough for
the Service to have developed a
standardized approach to permitting
and ensure permitting is consistent with
the preservation standard. These
regulations also restructure the existing
specific permit regulations. These
regulations apply, regardless of whether
infrastructure is constructed before or
after the final regulations.
We amend these regulations to better
align with the purpose and need
described in the 2016 PEIS. In the 2016
Eagle Rule, the Service sought to:
(1) increase compliance by
simplifying the permitting framework
and increasing certainty;
(2) allow for consistent and efficient
administration of the program by
Service staff;
(3) regulate based on best available
science and data; and
(4) enhance protection of eagles
throughout their ranges by increasing
implementation of avoidance,
minimization, and mitigation of adverse
impacts from human activities.
In this rulemaking, we create a new
subpart E for regulations governing the
permitting of eagle take for other
interests. We adopt two regulations for
administering permitting: specific
permits (§ 22.200) and general permits
Under these new and updated
regulations, the Service will authorize
eagle take using general permits and
specific permits. General permits
simplify and expedite the permitting
process for activities that have relatively
consistent and low risk to eagles and
well-established avoidance,
minimization, and compensatory
mitigation measures. General-permit
applicants self-identify eligibility and
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register with the Service. This includes
providing required application
information and fees and certifying that
they meet eligibility criteria and will
implement permit conditions and
reporting requirements.
The Service will implement general
permits for the following activities: (1)
certain categories of bald eagle nest take,
(2) certain activities that may cause bald
eagle disturbance take, (3) eagle
incidental take associated with power
line infrastructure, and (4) eagle
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§ 22.200
§ 22.210
§ 22.215
§ 22.220
§ 22.250
§ 22.260
§ 22.280
§ 22.300
§ 22.325
§ 22.400
incidental take associated with certain
wind energy projects. These are
described in more detail in the
following sections. The Service will
audit general permits to ensure
applicants are appropriately interpreting
and applying eligibility criteria and
complying with permit conditions.
Audits will include reviewing
submitted application materials and
reports. The Service will also request
and review any plans or strategies
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required by permit conditions, like
adaptive management plans.
The Service will continue to issue
specific permits, which require
submission of application materials to
the Service for review and development
of permit conditions. To maintain a
review process adequate to meet the
preservation standard for eagles, the
Service retains the specific-permit
approach for situations that have
increased or uncertain risks to eagles.
The applicant is responsible for
submitting a qualifying application. The
Service will determine, based on the
materials provided, whether the
application meets regulatory
requirements. The Service is responsible
for identifying and using the best
available information in making these
determinations. If an applicant is unable
to meet Service data standards in
applying, the Service may waive these
data standards provided: (1) the
application otherwise meets issuance
criteria, (2) the Service has adequate
information to estimate take, and (3) the
waiver will be consistent with
preservation of the eagle species. There
is no process to petition the Service for
a waiver; rather, this process will be at
the Service’s discretion and
documented in the permit file. Specific
permit conditions must meet or exceed
the requirements of general permits,
except when not practicable or when
site-specific data warrants
customization.
If the best available information
indicates that continuing
implementation of a general permit
program is inconsistent with the
preservation of bald eagles or golden
eagles, the Service may suspend the
general permit program temporarily or
indefinitely. This suspension may apply
to all or part of general-permit
authorizations. Consistent with 50 CFR
part 21 and part 22 permitting, Tribes or
States may choose to be more restrictive
than Federal regulations. Permittees
must comply with Tribal and State laws
and regulations to be in compliance
with Federal eagle permits.
Eagle Incidental Take Permits for Wind
Energy
With this rulemaking, the Service
seeks to implement efficiencies in
authorizing incidental take associated
with wind energy projects. This final
rule creates a general permit option for
projects in areas that are low risk to
eagles. We also revise the specific
permit process to provide clarity to
applicants and ensure processing is
efficient and consistent with the
preservation standard. With broader
participation in permitting, the Service
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anticipates increased benefits to eagle
populations as more projects implement
avoidance, minimization, and
mitigation measures.
The Service uses a combination of
eagle relative abundance and proximity
to eagle nests as eligibility criteria for
wind energy general permits. The
Service uses the Cornell Status and
Trends definition of relative abundance
and relative abundance products
(Cornell Lab of Ornithology, Ithaca, New
York, available at: https://
science.ebird.org/en/status-and-trends).
Relative abundance values determined
for a project must be based on these
publicly available Status and Trends
relative abundance products for bald
eagles and golden eagles. To help
project proponents quickly determine
eagle relative abundance, the Service
will maintain an online mapping tool
(https://arcg.is/CKLKy1).
For first-time applicants, generalpermit eligibility is based on eagle
relative abundance and proximity to
eagle nests at the time of application.
All turbines must be located in an area
with eagle relative abundance less than
the threshold identified by regulation
(§ 22.250(c)(1)(ii) for both bald eagles
and golden eagles). All turbines,
including the space occupied by blades
or other turbine infrastructure, must
also be located at least 2 miles from a
golden eagle nest and at least 660 feet
from a bald eagle nest (§ 22.250(c)(1)(i)).
Project proponents are expected to
survey for eagle nests with due
diligence and in accordance with any
Service guidance for nest surveys.
The Service considered allowing
general permit applicants to select
authorization for just one species. By
requiring both species, the Service is
able to reduce administration costs and
keep the general permit process simple.
Both species are widely distributed and
co-occur in most States. The Service
recognizes that the risk to each species
is not uniform, and we factored in the
relative risk to each species into the
relative abundance criteria, the nest
buffers, and the compensatory
mitigation requirements.
The Service added an eligibility
criterion for wind energy projects that
are renewing a general permit
(§ 22.250(c)). A general permittee
remains eligible to renew their permit,
even if the Service revises eagle relative
abundance thresholds or eagles
construct a nest within the speciesspecific setback distances, as long as the
project remains in compliance with all
other general permit requirements. This
includes provisions regarding the
discovery of eagle remains or injured
eagles remaining fewer than four eagles
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of the same species within a 5-year
permit tenure (§ 22.210(b)(2)(i)). This
eligibility applies to the turbines
authorized under the original general
permit and does not apply if there was
a lapse in permit coverage or if any
turbines are added to the project. It does
apply if the turbines change ownership.
If a project adds turbines, the new
turbines must meet the qualifications for
a first-time general permit
(§ 22.250(c)(1)) when renewing a general
permit for a project. If there is a lapse
in coverage, the project must qualify for
a first-time general permit
(§ 22.250(c)(1)) and may then renew
(§ 22.250(c)(2)), if eligible, or apply for
a specific permit.
The Service acknowledges that
existing wind projects have less ability
to adapt to the location-based nature of
the general permit eligibility criteria (as
defined in § 22.250(b)). After extensive
review, the Service could not identify
general permit eligibility criteria with
which a project could self-certify that
did not add extensive complexity or
uncertainty. However, the Service
retained the proposed eligibility
criterion that any existing project that
does not meet general permit eligibility
criteria can submit an application for a
specific permit (§ 22.200(b)) and request
a letter of authorization to obtain a
general permit (§ 22.250(c)). The Service
will review all information provided in
the application, including any sitespecific, pre- or post-construction data.
The Service will issue a letter of
authorization to apply for a general
permit if we determine that the take
rates at the existing project are likely to
be consistent with or lower than eagle
take rates expected at similar-sized
wind facilities that qualify for general
permits. If an applicant receives a letter
of authorization, we may refund the
specific-permit application fee, but to
cover the cost of review, we will not
refund the administration fee. The letter
of authorization may require additional
avoidance, minimization, or
compensatory mitigation requirements
if appropriate (for example, when
needed to ensure consistency with
general permit take rates).
The Service estimates that more than
80 percent of existing land-based wind
turbines in the lower 48 States may be
eligible for general permits. Wind
projects in Alaska, Hawaii, island
territories, and the offshore environment
should apply for a specific permit if
authorization for eagle incidental take is
sought. Authorization for incidental
take due to power line infrastructure is
not included under a general permit for
wind. The Service expects wind projects
to avoid risk to eagles by ensuring
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power line infrastructure is avian-safe,
either by design or use of covers. In the
rare circumstance associated power line
infrastructure poses an electrocution or
collision risk to eagles, authorization
under the power line regulation is most
appropriate. Specific permits are
available for wind projects that do not
meet general permit eligibility criteria or
request the customization of a specific
permit. We have created multiple tiers
within specific permits: Tier 1, Tier 2,
and Tier 2 with reimbursable agreement.
Changes to the fee structure associated
with these tiers are described in the
Changes to the Fees section below. Tier
1 specific permits are for lowcomplexity wind project applications
(1) that can comply with general permit
conditions or require only minor
modifications, (2) where fatality
estimates can be calculated with sitespecific data collected to Service
standards and submitted using the
Service’s information reporting template
or where the applicant agrees to use the
Service’s generalized fatality estimation
process (i.e., using the nationwide
specific permit priors) for specific
permits, (3) that agree to use a Serviceapproved conservation bank or in-lieu
fee program to complete required
compensatory mitigation, and (4) where
the Service’s decision can be
categorically excluded under NEPA.
The Service anticipates expediting Tier
1 specific permit application processing.
Tier 2 specific permits are for
moderately complex applications that
(1) need modifications to general-permit
conditions, including negotiated
compensatory-mitigation requirements
or (2) for which fatality estimation
requires more evaluation of site-specific
data, or (3) negotiation of other
requirements. For the highest
complexity applications, such as
applications that require more extensive
permit-condition negotiations, cannot
be categorically excluded from
additional procedural requirements of
NEPA, or other unique circumstances,
the Service will charge the Tier 2 fee
and require applicants, including
government agencies, to enter into a
reimbursable agreement with the
Service to offset additional Service costs
associated with this added complexity
and review time in excess of 275 hours.
The Service will no longer specify an
authorized number of eagles that may be
incidentally killed or injured on the face
of general or specific permits. Permits
will authorize the incidental take of
eagles. This means that permittees will
not be considered out of compliance for
exceeding an authorized level of eagle
take. General permittees, however, must
remain in compliance with the
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discovered eagle provisions, which are
different from estimated eagle take.
However, to ensure consistency with
our preservation standard, we will
estimate the number of eagles taken for
internal tracking and calculating
compensatory mitigation requirements.
The Service will track estimated take
that has been authorized for bald eagles
and golden eagles within each eagle
management unit (EMU) and local area
population (LAP). We will use the bestavailable information and tools in
making these calculations, including
compiling information on discovered
eagle remains and injured eagles,
applying statistical modeling to estimate
eagle take that has been authorized
under permits, and comparing estimated
take and provided compensatory
mitigation with EMU take limits and
LAP thresholds.
The Service received numerous
comments regarding the Service-led
monitoring in the proposed rule. The
Service reexamined the potential of
using operations and maintenance staff
to conduct concurrent monitoring
instead. Ultimately, we decided to
reduce the requirement for general
permits to concurrent monitoring
because that will still provide the
information the Service requires while
resulting in a substantial cost savings to
the regulated community compared to
the proposed Service-led monitoring.
The Service intends to publish
monitoring standards for specific
permits that will be designed to
maximize flexibility to the regulated
community so permittees can select the
best fatality monitoring method for their
project, while still giving the Service the
information needed to ensure we are
authorizing take consistent with our
preservation standard. Monitoring must
be conducted in accordance with permit
conditions and, if available, Service
guidance. The Service may use
administration fees to validate
concurrent monitoring methods and
analyze concurrent monitoring data.
Under specific permits, additional
monitoring may be included in the
permit conditions, such as for
permittees wanting to reduce mitigation
requirements by implementing
experimental technology or postconstruction monitoring. The Service
will require only third-party monitoring
when warranted (e.g., addressing
compliance concerns or applying
controversial approaches).
Compensatory mitigation is required
for general permits. General permits
must obtain eagle credits from a Serviceapproved conservation bank or in-lieu
fee program based on the hazardous
volume of the project (§ 22.250(f)(7)(ii)).
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An eagle credit is the amount of
compensatory mitigation needed to
offset the take of an eagle. Serviceapproved in-lieu fee programs and
conservation banks will be authorized
for particular EMUs, consistent with the
methodology approved by the Service.
However, the Service will retain the
right to direct funds from an EMU-scale
to an LAP-scale, if the Service identifies
concerns with a particular LAP.
Compensatory mitigation is also
required for specific permits for wind
energy. Applicants must include their
expected method of compensatory
mitigation in the permit application
(§ 22.250(f)(7)(i)). The Service will
derive the amount of compensatory
mitigation required using a projectspecific fatality estimate, based upon
either site-specific data that meets the
Service’s data collection standards or
the Service’s generalized fatality
estimation process (i.e., using the
nationwide specific permit priors).
These priors are probability
distributions, created using information
from a range of projects under Service
review and others described with
sufficient detail in Whitfield (2009), that
describe exposure and collision
probability in the Service’s collision risk
model before any site-specific
information is taken into account. All
compensatory mitigation for golden
eagles must be performed at a 1.2:1
(mitigation:take) ratio. The Service
expects Tier 1 specific permits to use a
Service-approved conservation bank or
in-lieu fee program to meet mitigation
requirements. Tier 2 specific permit
applications may use a Serviceapproved conservation bank or in-lieu
fee program or submit a plan to the
Service for implementing compensatory
mitigation consistent with § 22.200 and
Service-wide mitigation policies. To
ensure consistency with the
preservation standard, wind energy
projects that are eligible for general
permits but choose to obtain a specific
permit will be required to meet or
exceed the general permit mitigation
requirements. Compensatory mitigation
is not required for wind turbine
infrastructure that is considered
baseline. Baseline, as described in the
2016 PEIS, refers to infrastructure that
existed and was operating in its current
configuration and size prior to
September 11, 2009.
The Service retains the maximum 30year tenure for specific permits for wind
projects. This tenure is appropriate
given the amount of time that wind
energy projects typically operate on the
landscape. Specific permits may be
requested and authorized for any
duration (in 1-year increments) up to 30
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years. General permits for wind projects
are valid for 5 years from the date of
registration. Upon expiration of general
permits, project applicants may reapply
and obtain a new 5-year general permit.
General permits for eagle take cannot be
amended during each 5-year term.
For both general and specific permits,
the Service will continue requiring
implementation of all practicable
avoidance and minimization measures
to reduce the likelihood of take. These
conditions would likely include
reducing eagle attractants at a site (e.g.,
minimizing prey populations or perch
locations), minimizing human-caused
food sources at a site (e.g., roadkill,
livestock), and implementing adaptivemanagement plans that modify facility
operations at a site if certain
circumstances occur, such as when a
certain number of eagle mortalities are
detected. General permit conditions will
be nonnegotiable and fixed for the term
of the permit. Renewed general permits
will have the most current version of
general permit conditions. Specific
permit conditions will use the general
permit conditions as a foundation but
may be modified or added to as
appropriate. The appropriate fee tier
will be charged based on the amount of
negotiation and modification required.
Permittees must train relevant
employees to look for, recognize, and
report eagle take as part of their regular
duties. Permit conditions will specify a
minimum frequency required (e.g., once
every 3 months) and require that trained
employees visually scan for injured
eagles and eagle remains while in the
vicinity of project infrastructure. Permit
conditions will direct disposal (e.g.,
shipped to National Eagle Repository)
and reporting (e.g., summary emailed to
the Service) requirements and timelines.
When three or four eagles of one
species are discovered within the
general permit tenure, we require
additional conditions. If three eagles of
one species are found, the permittee
must notify the Service and implement
an adaptive management plan. If a
fourth eagle of that same species is
found, these steps must be repeated, and
the project would no longer qualify for
future general permits. The discoveredeagles provision aids in identifying the
rare project eligible for a general permit
but experiencing more take than other
projects covered by general permits. By
requiring notification from projects
operating under general permits if three
and four eagles are found, we ensure
that the overall take authorized by the
general-permit program remains within
the range we predict and is
appropriately offset to the degree
necessary for the preservation of each
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eagle species. It is important to note that
found eagle remains at any project
represent only the minimum number of
eagles that may have been killed by a
project. Depending on the probability of
detection, which is determined by
factors like site topography and
vegetation, the number of eagles
actually taken may be close to the
number of eagles found, or the number
actually taken could be substantially
higher.
We will allow time for project
proponents to adjust to these amended
regulations. Project proponents who
have submitted a permit application
will have 6 months from the publication
date of the final rule to choose whether
to have their application reviewed and
administered under all the provisions of
the prior regulations, as amended in
2016, or all the provisions of the current
regulations. Any application fees paid
prior to the publication date of the final
rule may be used to pay for application
and administration fees required under
the new regulations. However, the
Service will not refund any application
fees paid prior to the publication date of
the final rule because the Service will
have already undergone substantial
processing of the application. Project
proponents who hold a permit under
the 2016 regulations may continue
under that permit’s conditions until the
permit expires. Permittees that want to
modify existing permits to comply with
current regulations may contact their
permitting office to determine if a
substantive amendment request or a
new application is most appropriate.
Eagle Incidental Take Permits for Power
Lines
Power line entities have expressed
interest in obtaining authorization for
eagle incidental take caused by
powerline infrastructure; however, a
number of barriers have limited
participation in permitting. We create a
general permit option for power line
entities that can comply with
standardized conditions. We also revise
the specific permit process to provide as
an option for power line entities that
require more customization. The Service
anticipates increased benefits to eagle
populations as more power line entities
obtain permits and implement required
avoidance, minimization, and
mitigation measures.
All power line entities are eligible for
general permits. The Service
recommends a general permit for any
power line entity that can comply with
standardized general permit conditions.
Specific permits are available for power
line entities that seek customized permit
conditions. We have created multiple
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tiers within specific permits: Tier 1, Tier
2, and Tier 2 with reimbursable
agreement. Tier 1 specific permits are
for low-complexity applications that
require minor modifications to the
general-permit conditions and where
the Service’s decision can be
categorically excluded under NEPA.
The Service anticipates expediting Tier
1 application processing. Tier 2 specific
permits are for moderately complex
applications that can be categorically
excluded from additional NEPA
procedural requirements and need
unique or substantive modifications to
the general-permit conditions, such as
negotiated compensatory mitigation
requirements. In the rare circumstance a
power line application exceeds 275
hours in review time, the Service will
charge the Tier 2 fee and require
applicants, including government
agencies, to enter into a reimbursable
agreement with the Service to offset
additional Service costs associated with
this added complexity and increased
review time exceeding 275 hours.
Exceeding 275 hours is expected only in
rare cases; for example, if the Service’s
decision cannot be categorically
excluded under NEPA or permit
conditions require extensive
negotiations.
The Service will not specify a number
of eagles authorized on the face of
general or specific permits. However,
the Service will use annual reports
submitted by permittees to estimate the
number of eagles taken for internal
tracking and to ensure consistency with
our preservation standard. We will use
the best-available information and tools
in making these calculations. The
monitoring required for general permits
and most specific permits will be
limited to concurrent monitoring by
operations and maintenance personnel
while onsite. Monitoring must be
conducted in accordance with permit
conditions and, if available, Service
guidance. The Service may use
administration fees to validate
concurrent monitoring methods and
analyze concurrent monitoring data.
Specific permits may require concurrent
monitoring or additional monitoring.
For both general and specific permits,
the Service will require implementation
of all practicable avoidance and
minimization measures to reduce the
likelihood of take. To aid in assessing
what measures are practicable to
implement, the Service will refer to the
Avian Power Line Interaction
Committee (APLIC) suggested practices,
including Suggested Practices for Avian
Protection on Power Lines: The State of
the Art in 2006 and Reducing Avian
Collisions with Power Lines: The State
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of the Art in 2012, as well as updated
versions or new suggested practice
documents, as they become available.
General permits for power line entities
include the conditions listed in
§ 22.260(d). Specific permit conditions
will use the general permit conditions
as a foundation but may be modified or
added to as appropriate. The
appropriate fee tier will be charged
based on the amount of negotiation and
modification required.
As part of general-permit conditions,
the Service requires power line entities
to develop four strategies: collision
response, proactive retrofit, reactive
retrofit, and shooting response, as
defined in § 22.260(b). The Service
encourages power line entities with an
Avian Protection Plan (APP) to
incorporate these strategies into the
APP. However, power line entities may
choose to include these four strategies
as part of an APP or as stand-alone
strategies.
Collision response strategy describes
the process to identify collision-caused
mortality events, evaluate factors, and
implement risk-reduction strategies (see
§ 22.260(b) and (d)). The Service expects
risk-reduction strategies to be
commensurate with future collision
risk. For example, an entity would
implement all practicable risk-reduction
strategies for a power-line segment with
repeat mortality events in a high-risk
location but for power-line segments
with rare or no known collision events,
no action or continued monitoring may
be appropriate.
Proactive retrofit strategy describes
how existing infrastructure will be
converted to avian-safe (as defined in
§ 22.260(b)) within a set timeline (see
§ 22.260(b) and (d)). Investor-owned
utilities must have a 50-year proactive
retrofit strategy to convert poles in highrisk eagle areas to avian-safe; therefore,
10 percent of poles in high-risk eagle
areas must be converted during each
general-permit 5-year tenure
(§ 22.260(d)(2)(i)). High-risk eagle areas
occur where eagles are likely to be
present and interact with power line
infrastructure. Conversely, low-risk
eagle areas occur where eagles are not
present or unlikely to interact with
power line infrastructure, such as urban
areas. Applicants will be responsible for
the assessment of high-risk eagle areas,
based on this standard. Other utilities
(publicly owned or cooperative) must
have a 75-year proactive retrofit strategy
to convert poles in high-risk eagle areas
to avian-safe; therefore, 7 percent of
poles in high-risk eagle areas must be
converted during each permit tenure
(§ 22.260(d)(2)(ii)). The Service uses the
U.S. Energy Information Administration
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definitions for investor-owned, publicly
owned, and cooperative utilities. The
Service recognizes that this strategy may
take more time than the other strategies
to develop. As a condition of the general
permit, general permittees that do not
already have a proactive retrofit strategy
will have 3 years from the effective date
of this final rule to develop one.
Reactive retrofit strategy describes
how infrastructure will be retrofit to
avian-safe in response to an eagle
electrocution or death (see § 22.260(b)
and § 22.260(d)). A total of 13 poles or
a half-mile segment of line must be
retrofit. The typical pole selection is the
pole that caused the electrocution and
six poles in each direction. However, if
retrofitting other poles in the circuit
provides more benefit to eagles, those
poles may be retrofitted by prioritizing
the highest risk poles closest to the
electrocution event. Poles outside of the
circuit that caused the electrocution
may be counted towards this retrofit
requirement only if all poles in the
circuit are already avian-safe.
Converting poles to buried line is an
avian-safe retrofit.
To implement the above strategies,
power line entities evaluate the
electrocution or collision incident
within 90 days and implement a
response within 1 year of the incident.
If extenuating circumstances occur in
implementing the strategies, such as
catastrophic weather, extensive fire, or
other event that substantively disrupts
power delivery, the power line entity
must do the following: (1) Document
and maintain records of the relevant
circumstances, including why
circumstances are extenuating and the
plan to implement the delayed retrofits
or collision reduction measures. (2) If
implementation of delayed retrofits or
collision reduction measures will
extend past the expiration of the current
general permit tenure and the permittee
wants to renew the general permit,
notify the Service at least 180 days prior
to permit expiration. (3) If the general
permit is renewed, any delayed retrofits
or collision reduction measures must be
implemented during the renewed
general permit tenure. Otherwise, the
permittee is no longer eligible for a
general permit; however, the permittee
may apply for a specific permit.
Shooting response strategy describes
the process the permittee follows when
eagles are found killed or injured near
power line infrastructure to identify if
shooting is suspected, communicate
with law enforcement, and identify and
implement appropriate shootingreduction strategies (see § 22.260(b) and
§ 22.260(d)). Power line entities are not
responsible for law enforcement of nor
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liable for shooting events. At a
minimum, power line entities must
immediately contact the Service’s Office
of Law Enforcement if an eagle is found
killed or injured near power line
infrastructure and shooting is suspected.
Where there are repeated shooting
events, the power line entity should
develop other strategies, including
coordinating with the relevant landmanagement agency if the death or
injury occurs on government property.
The Service is working with APLIC and
others to develop resources and
suggested practices. It is generally
assumed that eagle remains or injured
eagles discovered in the vicinity of
power line infrastructure are taken by
that power line infrastructure, unless
necropsy or other information proves
otherwise.
In addition to the above strategies,
power line entities must also consider
eagles in siting and design for new
construction and rebuild projects and
ensure that all poles constructed in
high-risk areas are avian-safe, as
practicable. This provision is not
required if it would impact human
health and safety, require overly
burdensome engineering, or have
significant adverse effects on biological,
cultural, or historical resources.
Permittees must also train onsite
personnel to scan for and appropriately
report discovered eagle remains. Under
specific permits, additional monitoring
may be required.
Compensatory mitigation is required
for both general permits and specific
permits. General permits must
implement a proactive retrofit strategy
(§ 22.260(d)(3)). Compensatory
mitigation for specific permits will be
determined for each application and
included in permit conditions
(§ 22.260(e)(2)). The Service will track
take that has been authorized for bald
eagles and golden eagles within each
eagle management unit (EMU) and local
area population (LAP).
General permits for power line
entities are valid for 5 years from the
date of registration. Upon expiration of
a general permit, a project applicant
may reapply and obtain a new 5-year
general permit. General permits cannot
be amended during each 5-year term.
The Service retains a maximum tenure
of 30 years for specific permits for
power line entities. The 30-year tenure
is appropriate given the extended time
power line infrastructure is expected to
operate on the landscape. Specific
permits may be requested and
authorized for any duration (in 1-year
increments) up to 30 years.
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Eagle Disturbance Take Permits
More than two-thirds of the eagle-take
permits the Service currently issues are
for incidental disturbance by activities
conducted near bald eagle nests.
Incidental take by disturbance is
different from incidental take resulting
in injury or mortality. To reduce
complexity and improve clarity, this
final rule creates a new stand-alone
regulatory section for the incidental take
of bald eagles or golden eagles by
disturbance (§ 22.280). This regulation
revises portions of the previous
disturbance-take regulation (50 CFR
22.80). The Service retains the existing
definition of ‘‘disturb’’ (50 CFR 22.6)
and clarifies further what does and does
not constitute disturbance take
(§ 22.280(b)).
The Service creates general permits
for eagle incidental take by disturbance
in § 22.280. The Service uses the
standardized approach to permitting
based on the 2007 Activity-Specific
Guidelines of the National Bald Eagle
Management Guidelines (hereinafter the
‘‘Guidelines’’). Between publication of
the Guidelines in 2007 and nationwide
eagle-population surveys in 2018, we
estimate that bald eagle populations
have quadrupled in the Lower 48
United States (USFWS. 2021. Final
Report: Bald Eagle Population Size:
2020 Update. December 2020. Division
of Migratory Bird Management,
Washington DC U.S.A.). This includes
growth into environments that are
developed or in the process of being
developed, increasing the demand for
permits for eagle disturbance. By
creating general permits, the Service
will better align the conservation value
gained from permitting with ensuring
the preservation of eagles. We estimate
about 85 percent of projects that cause
disturbance will qualify for general
permits.
General permits are available for the
disturbance of bald eagles when the
disturbance will be a result of one or
more of the following activities:
building construction, linear
infrastructure construction and
maintenance, alteration of shorelines
and water bodies, alteration of
vegetation, motorized recreation,
nonmotorized recreation, aircraft
operation, prescribed burn operations,
and loud intermittent noises. General
permits cover conducting the activity, as
well as pre-construction work,
including geotechnical work. The
Service did not include prescribed-burn
operations in the proposed rule because,
at the time, we considered such
activities part of alteration of vegetation.
However, after considering public
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comment on the issue and to ensure
clarity for the regulated community, we
included prescribed burning as a
potential disturbance activity in the
final regulation. Prescribed burning
includes the footprint of the burn as
well as where biproducts of the burn
will be present, such as smoke, ash, or
embers. Specific permits are available
for disturbance to bald eagles from
activities that are not eligible for general
permits and any activity that may result
in disturbance to golden eagles.
The Service specifies distances in the
regulation within which these activities
may cause disturbance. Activities
occurring farther than the distances
specified below do not require a permit
because they are unlikely to cause
disturbance. Regularly occurring
activities that occur within these
distances and pre-date an eagle pair’s
selection of a given nest site are
assumed tolerated by the eagles,
unlikely to cause disturbance, and do
not require a permit.
Tribes communicated concern about
the issuance of general permits for nest
disturbance and nest take on lands of
Tribal interest. In response, the Service
has restricted eligibility, and general
permits are not available for nest
disturbance or nest take for nest
structures located in Indian country, as
defined in 18 U.S.C. 1151. The Service
considers the case-by-case review of
specific permits appropriate for nests
located in Indian country. This
restriction does not apply when the
Tribal government is the applicant for
the permit on their own land.
Hazing—the use of nonlethal methods
to disperse eagles away from a site—
does not constitute eagle disturbance
unless it is adjacent to an in-use nest
and disrupts eagle breeding activity.
The intent of hazing is to deter eagle
depredation (e.g., substantial injury to
wildlife or agriculture) or reduce threats
to human or eagle health and safety by
temporarily displacing individual eagles
from a location. We currently
recommend nest buffers of 660 feet for
bald eagles and 1 mile for golden eagles.
The Service also considers activities
that are conducted adjacent to a
communal roost or foraging area do not
constitute eagle disturbance and do not
require a permit. ‘‘Communal roost site’’
and ‘‘foraging area’’ are defined by
regulation (50 CFR 22.6). Removal of a
foraging area has greater potential to
cause disturbance; therefore, we further
clarify here that activities that
completely prevent the use of a foraging
area may cause disturbance. A
proponent of a project likely to fully
prevent the use of a foraging area should
apply for a specific permit, particularly
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if the activity will remove all foraging
opportunities within 1 mile of an in-use
nest.
The Service will require monitoring
eagles under general and specific
disturbance-take permits. Monitoring
will typically consist of collecting
information sufficient to determine
whether nestlings have fledged from the
nest. Specific permits for disturbance
may require monitoring as long as
necessary to determine any impacts to
the eagles for which take is authorized,
including up to 3 years after permit
tenure. The Service does not require
compensatory mitigation for general
permits. Compensatory mitigation may
be required for specific permits to
ensure the preservation of eagles. For
example, any disturbance take of golden
eagles that is not part of the Service’s
previously established 2009 baseline or
disturbance take of bald eagles that
exceeds the LAP authorized-take
threshold and is otherwise
unsustainable requires implementation
of compensatory mitigation. Monitoring,
and if required, compensatorymitigation outcomes must be reported
annually.
For both specific and general
disturbance permits, we will require
that applicants provide the coordinates
of the nest(s) for which they are
requesting disturbance authorization.
Precise location information is
necessary for both the Service staff who
conduct eagle-population management
and law enforcement. For disturbance
take, we retain a 5-year tenure for
specific permits and implement a 1-year
tenure for general permits. These
permits are renewable in the rare
circumstance that an activity is likely to
cause disturbance to eagles over a long
period of time. In the rare event that the
Service’s decision to issue a disturbance
specific permit cannot be categorically
excluded under NEPA, a reimbursable
agreement may be used to cover costs
associated with the preparation of an
environmental analysis and compliance
with the procedural requirements of
NEPA.
For both specific and general permits,
we require permit conditions that
include implementation of measures to
avoid and minimize, to the extent
practicable, the risk that authorized
activities may disturb eagles. To
determine practicability, the Service
will consider eagle-population status,
the known efficacy of the measure, and
the potential burden on the permittee.
For specific permits, applicants will
have the opportunity to provide input
into these permit conditions. Generalpermit conditions will be standardized
by activity type based on effective
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techniques that have been consistently
and successfully used in specific
permits for the past 10 years or more.
The Service uses this rulemaking to
clarify that the regulations for
disturbance take of eagles will be used
to authorize the incidental take of eagle
nests. Incidental take of nests caused by
activities includes actions that agitate or
bother eagles to a degree that interferes
with normal breeding and sheltering
behavior. For example, prescribed burns
may result in the disturbance of
breeding eagles through smoke exposure
and may disrupt breeding activity by
unintentionally taking nests when a fire
moves unexpectedly across break lines
or into tree canopies. Authorization is
provided only for incidental take of
nests that occurs after application of all
practicable avoidance and minimization
measures. Incidental take authorization
does not include take caused by lack of
due diligence or negligence; for
example, failure to identify nest
locations prior to conducting an
activity.
To date, incidental take of nests has
been a rare issue and, therefore, is
currently most appropriately addressed
under specific permits. However, the
Service will regularly review this issue
with other implementation decisions.
Applicants requesting incidental take of
nests must demonstrate that incidental
nest take cannot be practicably avoided.
The Service does not anticipate
authorizing the incidental take of nests
for development activities. In the
Service’s experience, developers have
sufficient knowledge of the landscape
and control of their activity to make
incidental nest take practicably
avoidable during development.
Eagle Nest Take Permits
The Service has revised the
regulations for eagle nest take (§ 22.300).
This final rule creates a general permit
for the take of bald eagle nests in certain
circumstances. We retain specific
permits for the take of any golden eagle
nest as well as for the take of bald eagle
nests that is not eligible for a general
permit. We also clarify that relocation or
obstruction of a nest constitutes nest
take.
We retain the four justifications for
authorizing eagle nest take, which are
emergency, health and safety, removal
from human-engineered structures, and
other purposes. We also add protection
of species on the List of Endangered and
Threatened Wildlife (§ 17.11) as a
purpose for eagle nest take. General
permits are limited to bald eagle nest
take for the purposes of emergencies,
protection of health and safety, and
protection of human-engineered
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structures. In Alaska only, bald eagle
nests may also be taken for other
purposes. After more than 10 years of
issuing permits to remove bald eagle
nests, the Service has developed
standard permit conditions that can be
applied to authorizing the take of bald
eagle nests using general permits for
these purposes.
We will continue to require specific
permits for any take of golden eagle
nests because these situations have
unique conditions that require sitespecific permitting and because of the
population status of golden eagles. We
will also continue to require a specific
permit for take of bald eagle nests under
the ‘‘other purposes’’ in the lower 48
States because the Service must ensure
that those permits provide a net benefit
to eagles. The net-benefit determination
depends on the circumstances of the
purpose requiring nest take. In Alaska,
general permits are appropriate because
the Service has already developed and
implemented standard conditions there
and Alaska has a robust bald eagle
population.
In this rulemaking, the Service adds a
fifth justification for authorizing the
take of eagle nests when necessary for
the protection of species on the List of
Endangered and Threatened Wildlife
(§ 17.11) under the Endangered Species
Act of 1973, as amended (16 U.S.C.
1531–1544). This activity would require
a specific permit issued only to a
Federal, State, or Tribal agency
responsible for implementing actions for
the protection of the species of concern.
With expanding bald eagle populations,
the Service anticipates an increase in
situations where bald eagle management
may be a necessary part of
implementing recovery plans.
The Service will not require
monitoring for general permits. After
more than a decade of annual
monitoring reports, we expect a 1-year
permit tenure to better capture the
necessary information to meet the
preservation standard than requiring
monitoring. In addition, a 1-year permit
term without required monitoring is less
burdensome to the applicant. Specific
permits may require monitoring—for
example, a permittee may need to
monitor the area near where a nest was
removed for one or more seasons to
determine whether the affected eagles
relocate and successfully fledge young.
To be conservative, we will assume that
each nest take authorized by the general
permit will result in a loss of breeding
productivity for one breeding season.
We may change this practice in the
future if data warrants a change in our
assumption.
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The Service will not require
compensatory mitigation for nest-take
general permits, unless it is for other
purposes in Alaska where compensatory
mitigation is required to achieve the
associated net benefit. General permits
for nest take are limited to bald eagle
nests in situations that are typically
hazardous to eagles or where eagles
benefit from resolving the situation
requiring the permit. Compensatory
mitigation is also not generally
warranted for nest-take general permits
because of the improving population
status of bald eagles. Compensatory
mitigation may be required for specific
permits. In determining compensatory
mitigation, the Service will consider the
purpose for the nest take, whether nest
take reduces risk to eagles, and the
population status of the species. A
specific-permit applicant may meet this
requirement by obtaining the Serviceapproved number of eagle credits from
a Service-approved conservation bank
or in-lieu fee program. The applicant
may also propose other types of
compensatory mitigation for Service
approval.
For both specific and general nest take
permits, we will require that applicants
provide the coordinates of the nest(s) for
which they are requesting take
authorization. Precise location
information is necessary for both the
Service staff who conduct eaglepopulation management and law
enforcement. The permit application
may also require supporting
documentation for certain types of
requests (for example, an arborist report
in the case of hazard-tree removal).
For nest take, we retain the 5-year
limit for specific permits and implement
a 1-year limit for general permits. These
permits are renewable. The Service
considered providing for a longer
general-permit tenure; however, doing
so would require that the Service
require further monitoring from all
general permittees that was inconsistent
with the purpose of general permits. We
have crafted these reduced tenure and
permit-per-nest requirements to better
ensure general permits for nest take are
compatible with the preservation of
eagles.
Permit conditions will include the
applicable regional-breeding-season
start date. Additionally, the general
permit will authorize the removal of a
specific nest. General permits may
authorize bald eagle nest removal from
the nesting substrate at the location
requested and the location of any
subsequent nesting attempts by the
eagle pair within one-half mile of the
location requested for the duration of
the permit if the subsequent nest re-
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creates the emergency, safety, or
functional hazard of the original nest.
Take of an additional eagle nest more
than one-half mile away requires an
additional permit.
Changes to Definitions and Procedures
As part of this rulemaking, we have
narrowed the definition of ‘‘eagle nest’’
to exclude nest structures on failed
nesting substrate. Previously, we
defined ‘‘eagle nest’’ to mean any
assemblage of materials built,
maintained, or used by bald eagles or
golden eagles for the purpose of
reproduction. We have added a
qualification that it must be possible for
eagles to reuse the nesting substrate for
breeding purposes. Nesting substrate
that, due to natural circumstances, is no
longer and will never again be available
to eagles for functional use will no
longer meet the regulatory definition of
an eagle nest. This definition of ‘‘eagle
nest’’ does not allow for modification of
alternate (unused) nest substrate to a
degree that prevents future breeding
activity. These activities will continue
to constitute nest take.
We revise this definition to address
uncommon but occasional instances in
which eagle nests or nesting substrate
are impacted by weather or other
natural factors to such a degree that they
become permanently unusable to eagles
for reproductive purposes. For example,
if a nest tree falls and the bald eagle nest
retains its structure, the nest would no
longer retain the official designation of
an eagle nest as the substrate was
substantively changed by the nest tree
falling. A permit is not necessary for
individuals and organizations to destroy
and remove materials that formerly held
the designation of an eagle nest but no
longer meet the definition. However,
individuals and organizations may not
collect these materials nor possess them
beyond what is necessary to dispose of
the nest. Eggs, feathers, and other eagle
parts are often naturally incorporated
into nests with time. The Eagle Act
prohibits possession, transportation,
and sale of these items, either
individually or in their incorporated
state with former nesting materials,
without Federal authorization.
We also have revised the definition of
‘‘in-use nest’’ to clarify that the eggs
referred to in the definition of in-use
nest must be viable. As with our
revision of the definition for ‘‘eagle
nest,’’ this change ensures that our
definition is more relevant to what is
biologically important to eagles.
Nonviable eggs may persist in a nest or
even become incorporated into a nest’s
structure. However, by their nature,
these eggs will not hatch. Under
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previous definitions, permittees have
been prevented from removing what is
otherwise an alternate nest because of
the presence of nonviable eggs outside
of breeding season. In implementing the
revised definition, the Service presumes
that eggs are viable unless the applicant
provides evidence to document
otherwise (e.g., absence of adults for
several days, presence of eggs out of
breeding season).
For clarity, we add a definition of
‘‘general permit’’ to 50 CFR part 22 to
distinguish general permits from the
definition of ‘‘permit’’ in 50 CFR 10.12.
We interpret the statutory language
requiring a permit to be procured from
the Service for take of bald eagles for
any purpose to include general permits
set forth in this document as well as the
more typical individual or specific
permits (see 16 U.S.C. 668a).
We clarify in the regulation pertaining
to illegal activities (50 CFR 22.12) that
obtaining an eagle permit of any type for
a continuing activity does not in and of
itself resolve take that occurred before
issuance of the permit. This provision is
currently in § 22.80(e)(8) but applies to
all of the regulations in part 22 and is
therefore better located in § 22.12. We
also have updated the definition of
‘‘eagle management unit’’ and include a
definition of ‘‘incidental take’’ to
improve transparency to the public and
general-permit applicants.
Along with this final rule, the Service
will also implement the three following
changes to our implementation of
incidental-take permits for eagles. We
will apply the baseline take for golden
eagles established in the 2009 EA
nationwide. Currently, baseline take for
golden eagles is limited to only west of
the 100th meridian. In the 2016 PEIS,
the Service conservatively assumed that
all authorized take of golden eagles east
of the 100th meridian should require
compensatory mitigation regardless of
whether the authorized take was
occurring prior to September 11, 2009,
and was considered part of the baseline.
However, recent information on the
population status of golden eagles in the
Eastern United States demonstrates that
this conservative restriction is not
necessary to ensure that take of golden
eagles is compatible with the
preservation standard, so we are
eliminating this unnecessary restriction.
We will also update the number of
bald eagles debited from EMU take
limits and LAP thresholds when
authorizing nest disturbance, based on
new information. Before this change, the
Service assumed a loss of productivity
equivalent to 1.33 bald eagles per year
for each authorized nest disturbance in
the United States, except in the
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Southwest, where we assumed a loss of
0.95 bald eagles per year. Based on
recent Service analysis of new
information, we will update the
nationwide debit from 1.33 to a value of
0.26 bald eagles per year. However,
because of low sample sizes in our
analysis, we are not updating the debit
in the Southwest, which will remain at
0.95 bald eagles per year.
Finally, we will remove the 10
percent threshold for unauthorized
mortality in a local area population
(LAP) that was introduced with the
2016 rulemaking. We have since
concluded that georeferenced data on
unauthorized eagle mortalities are
sparse and biased, making meaningful
evaluation and application of
unauthorized take at the LAP scale
difficult or impossible.
Changes to Fees
The Service charges application fees
to cover the costs of administering
regulations and permits. This includes
paying for staff to: provide technical
assistance and guide applicants through
the permitting process, review
application information, assess the
biological impact and environmental
effects of the proposed activity, and
evaluate whether the applicant meets
eligibility and issuance criteria. For
specific permits, these actions are
primarily conducted before permit
issuance. For general permits, these
actions will be conducted as part of an
auditing process to ensure applicants
are correctly interpreting eligibility
criteria and complying with permit
conditions and requirements. Fees are
also used to pay for developing and
maintaining an online permitregistration system and database.
General-permit fees include an
administration fee. In response to public
comments, the Service adjusted the
administration fee to reflect the
elimination of the proposed Service-led
monitoring. Instead, the administration
fee will be used to maintain and groundtruth the permit program to ensure it is
compatible with the preservation of
eagles, including to: (1) better
understand eagle population dynamics,
including the risk to eagles from
authorized activities; (2) better
understand mitigation outcomes,
including researching and validating
avoidance, minimization, and
compensatory mitigation measures; (3)
address and improve various
components of the eagle permitting
program, including gathering and
analyzing demographic data, GPS
tagging and tracking eagles for
programmatic monitoring, and
researching and validating monitoring
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measures. Some portion of the
administration fees may also be used, as
necessary, to fund Service staff time to
manage and implement the general
permit administration fees. Specificpermit fees also include an
administration fee. We will use the
administration fee for specific permits
for the same purpose as application
fees—to fund staff for the administration
of specific permits, including
environmental review and support of
the online permit system and database.
The permit fee and administration fee
must be paid at the time of application.
We consider permit renewals to be
permit applications for fee purposes.
General permits cannot be amended.
However, specific permits may be
amended during their tenure. There are
three types of amendments.
Administrative amendments are
administrative changes, including name
and address information. Consistent
with § 13.11(d)(5), there is no fee
charged for administrative amendments.
Substantive amendments are those that
pertain to the purpose and conditions of
the permit. Consistent with
§ 13.11(d)(5), we will charge an
amendment fee. The Service will charge
an amendment fee and an
administration fee for permitteerequested substantive amendments that
require new analysis, such as
modifications that result in reestimating take, re-evaluating
compensatory mitigation requirements,
or requiring additional environmental
review to comply with procedural
requirements under NEPA (§ 22.200(e)).
For general permits, the Service
adopts a scaled administration-fee
structure to accommodate different sizes
of projects. For power lines, generalpermit administration fees are separated
into Tier 1 for non-investor-owned and
Tier 2 for investor-owned. The Service
uses the U.S. Energy Information
Administration’s definition of investorowned utilities as ‘‘large electric
distributors that issue stock owned by
shareholders’’ (https://www.eia.gov/).
For wind energy, general-permit
administration fees are separated into
Tier 1 for distributed and community
wind projects and Tier 2 for utility wind
projects. We use the Service’s LandBased Wind Energy Guidelines
definition of these terms (https://
www.fws.gov). The Service may revise
the interpretation of these terms in
future rulemakings.
The Service retains the existing tiers
of commercial and noncommercial for
disturbance and nest-take permits.
Applications are commercial, unless (1)
an individual applies using section A of
the application form for activities on
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that individual’s privately owned
property for individual purposes, or (2)
a government or not-for-profit entity
applies for take associated with public
property using section B of the
application form and includes
documentation demonstrating its
qualifying status (e.g., documentation
that the entity is a government agency
or that the entity is a current, recognized
nonprofit organization by the Internal
Revenue Service (IRS) as described in
section 501(c)(3)).
For specific permits, the Service
estimates a wide range of potential
permit costs. Costs would vary based on
factors like the complexity of the
application or the required
environmental review. To accommodate
this wide range, the Service includes a
tiered fee structure in § 13.11(d) and
describes criteria for each tier in
§ 22.200(c)(2)(vii) and below. For
incidental take, the Service will charge
a Tier 1 application fee when specificpermit conditions require negligible
modification from the standardized
general-permit conditions, including the
use of a Service-approved in-lieu fee
program or conservation bank for
compensatory mitigation. Tier 1 permits
would require Service staff to review
and evaluate the application and
coordinate internally prior to permit
issuance. We do not anticipate requiring
additional environmental compliance
review under NEPA for Tier 1 specific
permits beyond documenting that the
action is within the scope of the existing
2016 PEIS and the 2023 EA issued with
this rulemaking. For wind energy or
other applications that require a fatality
estimate, Service estimation of expected
take must require minimal data
manipulation; for example, the
applicant collects site-specific data
according to Service standards or adopts
the Service’s generalized fatality
estimate (i.e., using the nationwide
specific permit priors).
The Service will assess a Tier 2 fee for
specific permits of moderate to high
complexity that cannot or do not wish
to meet the requirements for Tier 1.
Because Tier 2 applications are more
complex, more staff hours, including
higher graded staff, are required to
review application information, assess
biological impacts and environmental
effects of the proposed activity, and
determine whether the application
meets eligibility and issuance criteria.
These projects may include more
complex technical assistance,
coordination with other programs or
agencies, and documenting NEPA
compliance. We estimate the amount of
staff time to complete these tasks for
moderately complex projects will be 250
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to 275 hours per permit based on
processing times for similarly complex
permits issued by the Service.
We retain the provision in
§ 13.11(d)(2) that allows an applicant to
request, and the Service to support,
issuance of one consolidated permit
when more than one type of permit is
required for an activity and those
permits are issued by the same office.
When the Service supports
consolidation, a single specific permit
may authorize multiple activities, for
example power lines with nest take or
wind energy with power lines. The
Service will develop guidance for
consolidating permits. Because of the
automated nature of general permits that
have avoidance, minimization, and
compensatory mitigation requirements
developed for each activity, a project
proponent would have to obtain the
relevant individual general permits.
Therefore, consolidating general permits
is not allowed.
The Service expects specific-permit
applicants to diligently pursue
obtaining a permit after applying. We
will consider a permit application
abandoned or withdrawn if an applicant
does not respond to requests for
information or engage in good-faith
negotiations. Once we consider an
application abandoned or withdrawn,
the applicant must submit a new
application, including fees, to obtain
take coverage for the activity.
Once effective, under this final rule
the Service will not charge an
application fee to government entities,
consistent with other permits issued in
accordance with § 13.11(d)(3); the
Service will charge an administration
fee to any Federal, Tribal, State, or local
government agency for permits issued
under part 22 subpart E. The Service
may also require government agencies to
enter into a reimbursable agreement.
This fee is necessary to ensure the
permitting program remains consistent
with the preservation of eagles.
Administrative Changes
The Service has made the following
administrative changes to the
organizational structure of our eagletake-authorization regulations to
improve clarity. To reduce confusion,
we redesignate the current subpart C
‘‘Specific Eagle Permit Provisions’’ as
‘‘Eagle Possession Permit Provisions.’’
We create a new subpart E pertaining to
‘‘Take of Eagles for Other Interests.’’
This subpart now houses regulations
that authorize permits for the taking of
eagles for the protection of other
interests in any particular locality.
We redesignate regulations for
permits to take golden eagle nests for
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resource development and recovery
operations from § 22.75 to subpart E, at
§ 22.325. We update the section heading
as ‘‘Golden eagle nest take for resource
recovery operations’’ to clarify that this
regulation applies to resource
development or recovery operations as
authorized by 16 U.S.C. 668a. The
purpose of this regulation is to authorize
the removal of golden eagle nests that
are physically in the way of resource
recovery operations, such as on the cliff
wall of a mine. We do not change the
regulatory requirements that any take
authorized must be compatible with the
preservation of eagles (newly designated
§ 22.325(c)) and cannot be reasonably
avoided (newly designated
§ 22.325(c)(1)). The take of nests in
proximity to resource development and
recovery operations to minimize the risk
of disturbance, injury, or mortality to
eagles is authorized under § 22.300. We
also redesignate the current regulations
at § 22.90 pertaining to permits for bald
eagle take exempted under the
Endangered Species Act to § 22.400 in
subpart E.
Sequencing of General Permits
Registration Availability
To implement the general permits
authorized under this rulemaking, the
Service is developing an online generalpermit registration system. After the
effective date of this regulation, April
12, 2024, the Service will implement the
general permit registration system in
stages to ensure the technology is
working appropriately. General permit
registration for incidental take of eagles
by wind energy projects and by power
lines is anticipated to be available
starting on May 6, 2024. General permit
registration for disturbance of eagles and
take of eagle nests is anticipated to be
available starting on July 8, 2024. In the
event these availability dates change,
the Service will provide updated dates
on https://www.fws.gov/regulations/
eagle and the ePermits website https://
epermits.fws.gov. Those interested in
applying for a wind energy or power
line general permit between the
effective date of the rule and the
availability of the registration system
may apply by: (1) completing
application form 3–200–71, including
sections B–D and the general permit
questions in section E and (2) emailing
the complete, signed form to
migratorybirdpermits@fws.gov. The
Service will reply to the email with the
general permit conditions. Entities must
comply with and are authorized by the
general permit conditions until the
registration system is available. Once
available, entities will have 10 business
days to register for a general permit
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using the registration system, including
paying fees. Failure to register, once
available, voids the prior coverage
granted through the above process.
For those interested in applying for
disturbance or nest take permits, the
Service will continue to use specific
permits for the remainder of the 2024
nesting season. For activities starting on
or after September 1, 2024, general
permits registration is expected to be
available. However, in the event it is
not, the procedure described in the
paragraph above will be used starting
July 8th until the registration system is
available.
Compliance With the Endangered
Species Act
The general permits addressed in the
regulations may not be used for an
activity if implementing the
requirements of the general permit may
affect ESA-listed species or species
proposed for listing or designated or
proposed critical habitat (e.g., burying a
cable to avoid impacts to eagles would
result in effects to an ESA-listed snake
or plant). In those cases, the proponent
should apply for a specific permit and,
if appropriate, the Service will conduct
an intra-service section 7 consultation
on its issuance of the eagle incidental
take permit. That said, since eagle
incidental take permits would authorize
only the incidental take of eagles and
not the underlying activity, except as it
relates to implementing the conditions
of the permit, the Service’s issuance of
an eagle incidental take permit would
not serve as a nexus for ESA section 7
purposes for the underlying activity.
Response to Public Comments
The Service received 203 unique
letters, which contained 1,649
individual substantive comments, on
the proposed rule. The following
sections contain a summary of the
substantive public comments we
received on the proposed rule and our
responses. Topics are listed in
alphabetical order. Where appropriate,
we explain why we did or did not
incorporate the changes suggested by
the commenters into this final rule. Due
to the high number of comments, this
summary presents major themes
occurring throughout the comments.
Not included are the many comments
providing general support for provisions
of the rulemaking. Likewise, we do not
include summaries of any comments
providing general opposition, unless
they contain suggestions for
improvement. We also do not respond
to comments that we considered to be
outside the scope of this rulemaking.
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Audits
Issue. Commenters requested more
information regarding the proposed
audit program, including details about
the auditing process, required
documentation, and expectations for
audited entities. Some comments
expressed concerns with the estimated
annual percentage of audited projects,
with many indicating a desire for more
projects to be audited annually.
Response. We are developing internal
auditing procedures and external
answers to frequently asked questions
on audits. Limited desktop audits and
onsite inspections will be conducted to
determine if a project meets eligibility
criteria and whether the permittee is
complying with the regulations and
permit conditions. In general, Service
staff will conduct an audit following
similar procedures to how staff
currently review a permit application
and administer permits. Audits may
include reviewing application materials
for completeness and general-permit
eligibility. We will verify required
reports were submitted and review the
reports. Any required records, plans, or
other documents will be requested of
the permittee and reviewed. If there is
a compliance concern, the applicant
will be given the opportunity to submit
additional information to address the
concern. If, during an audit, the Service
determines that the permittee is not
eligible for a general permit or is out of
compliance with general permit
conditions, we will communicate to the
permittee options for coming into
compliance.
The Service has estimated the number
of audits that can be conducted each
year based on the expected average time
to conduct an audit and the fee money
available to fund staff to conduct audits.
Staff will conduct as many audits as
possible with the available funds. There
are many uncertainties right now as to
how much staff time is needed to
conduct an audit. We estimate
approximately 1 percent of general
permits will be audited each year. If we
find general permittees are providing
complete information, audits may go
quickly and more projects can be
audited. We will regularly assess the
cost-per-audit and the percentage of
projects audited to adjust the fee
structure accordingly.
Avoidance and Minimization Measures
Issue. Several commenters expressed
concern with a lack of specificity in the
regulation regarding avoidance and
minimization measures.
Response. The role of regulation is to
establish performance standards,
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whereas the role of permit conditions is
to provide specificity on how those
performance standards may be met by
each permittee. Overly prescriptive
regulations are difficult to keep current
and can limit innovation. Instead, we
will provide permit conditions and
other documents to communicate the
Service’s recommendations on how to
meet regulatory requirements.
Avoidance and minimization
requirements for general permits are
based on the most commonly applied
and effective measures learned by the
Service from more than a decade of
permitting. Eligibility criteria and the
performance standards established in
the regulation conditions can be revised
through rulemaking. As information and
technology change, the Service may
update our recommendations and
expectations on how eligibility criteria
and conditions may be met.
Issue. Some commenters expressed
the desire to see permit conditions that
incorporate the use of experimental or
emerging technology to avoid and
minimize incidental take by wind
energy projects, including Identiflight
Bird Detection System, painting one
turbine blade black, or seasonal
restrictions on wind turbine operation.
Response. The Service supports
science and technology that increases
safe eagle passage through wind energy
facilities. There is no restriction on
permittees implementing these
technologies, which can be used to meet
the performance standards of the
regulation. However, the efficacy of
these technologies and the details
surrounding their implementation have
not been sufficiently studied to warrant
prescriptive requirements in these
regulations at this time. The Service
continues to stay abreast of scientific
developments and may include these
types of technologies in future
rulemakings if evidence demonstrates
their effectiveness. Specific permit
applicants may request that the Service
consider the permittee’s use of emerging
technologies when the Service estimates
fatality.
Issue. We received requests to include
perch discouragers as a standard
avoidance and minimization measure
for power line poles.
Response. We did not require perch
discouragers as a minimization measure
for power line general permits because
the effectiveness is situation dependent.
We encourage the use of perch
deterrents where they may be effective.
However, APLIC has moved away from
broad implementation of perch
discouragers because devices installed
to prevent perching may provide a
substrate to secure nest material, and, in
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some cases, may increase electrocution
risk (APLIC 2023). Prather and Messmer
(2010) tested several types of perch
discouragers and found no difference in
perching on poles with or without
discouragers. However, we support the
use of perch discouragers in situations
where it is the best or only option for
reducing electrocution of eagles.
Issue. Multiple commenters requested
that we create ‘‘no go zones’’ or similar
restrictions prohibiting the installation
of wind turbines in the most important
areas for eagles.
Response. The Service did not create
‘‘no go zones’’ because doing so is
outside the scope of the Eagle Act. The
Service’s authority under the Eagle Act
allows the regulation of incidental take
of bald eagles and golden eagles. Our
regulatory authority does not extend
beyond that mandate to prohibit the
installation of wind turbines or other
infrastructure. The Eagle Act ensures
the preservation of our two eagle species
by protecting the survival and breeding
productivity of individual birds but
does not directly mandate protection of
eagle habitat. Consequently, the Eagle
Act does not give the Service authority
to prohibit certain types of land use,
including development. Instead, it
allows us to influence certain types of
land use to reduce the risk of take of
bald eagles and golden eagles, including
disturbance of breeding eagles, and to
require avoidance, minimization, and
compensatory mitigation from
individuals and entities unable to avoid
taking these species. These features of
our regulatory process are common to
both existing regulations and these new
regulations.
Climate Change
Issue. The Service received comments
regarding the implications of climate
change for this rulemaking and the
inclusion of climate change in the EA.
Response. The Service recognizes the
threats that climate change poses to
eagles as well as other wildlife. The
Service supports all actions that address
climate change, including renewable
energy development. The Service
believes that this rule will help facilitate
the development of renewable energy
projects by revising the current
permitting approach for eagle incidental
take. The permit framework developed
for renewable projects creates clear
expectations for projects to achieve
compliance, in some cases with no
direct interaction with the Service (e.g.,
general permits). The Service is
balancing the need for regulatory
certainty, eagle preservation, and the
need for renewable energy development
to combat climate change. While we
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9931
intend the changes to the eagle-permit
regulations to encourage more projects
to apply for a permit, we expect that this
rulemaking will have no impact on the
number of future renewable energy
projects on the landscape and, thus, no
impact on the trajectory of climate
change.
Compensatory Mitigation
Issue. The Service received numerous
comments related to compensatory
mitigation requirements, including
advocating for different methods to
achieve these requirements, including
lead abatement, carcass removal from
roads, and habitat enhancement.
Response. The Service is actively
working on reviewing and approving
other forms of mitigation and
encourages potential mitigation
providers to submit their proposals. As
part of this rule, we created a new
regulation specific to compensatory
mitigation to more clearly signal
requirements to the public. Quantifying
the benefits of various compensatory
mitigation measures and developing
standards for their application in
permitting is complex. To date, the
Service has authorized power pole
retrofits and lead abatement as
compensatory mitigation measures. The
Service is actively developing other
compensatory mitigation methods, such
as roadside carcass removal, that will
decrease eagle mortality or increase
eagle productivity. The Service
encourages interested mitigation
providers to contact the Service with
ideas on compensatory mitigation
methods. The Service agrees that it is
important to develop compensatory
mitigation methods that offset different
sources of mortality and have a wider
range of mitigation providers across the
country. We will continue to engage
stakeholders and develop additional
guidance and standards for approving
mitigation providers. This will include
gathering information to address
mitigation measure effectiveness and
uncertainty and establishing appropriate
assurances for the durability of
mitigation measures.
Issue. Some commenters expressed
concerns with scaling compensatory
mitigation at the Eagle-ManagementUnit (EMU) level rather than the localarea-population (LAP) level.
Response. The final rule retains the
requirement to site compensatory
mitigation within the same EMU where
the take is authorized. Authorized take
may affect individual eagles that are
both resident and migratory. Banding
records have demonstrated eagle
movements within EMUs beyond
individual LAPs. Thus, requiring that
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compensatory mitigation occur at small
scales (e.g., the LAP scale) may be
limiting the benefits of compensatory
mitigation unnecessarily and doing so at
an inappropriate ecological scale.
Additionally, limiting compensatory
mitigation options to the LAP scale is
currently not practicable until there are
sufficient mitigation providers capable
of supporting every LAP. When
compensatory mitigation is required by
the Service to address an LAP concern,
the regulation prioritizes implementing
compensatory mitigation in the LAP
where the impacts occurred.
Issue. Several commenters expressed
concerns with requiring compensatory
mitigation for bald eagles and indicated
this requirement is not necessary to
meet the preservation standard.
Response. The general-permit
compensatory mitigation requirement
includes a small portion for bald eagles.
This is necessary to ensure that the
general-permit program is consistent
with the preservation standard
established by the Eagle Act and
implementing regulations. General
permits do not provide for the projectspecific review prior to issuance;
therefore, possible LAP effects must be
addressed after issuance. One tool is to
require a small amount of compensatory
mitigation from general permittees that
the Service can direct to areas where
LAP thresholds are at risk of being
exceeded. The rate of this extra
compensatory mitigation is based on
bald eagle take predictions, but the
mitigation amounts provided can be
used for either species of eagle. If an
applicant does not want to pay this
extra mitigation cost, which the Service
expects to be relatively small for each
project, the applicant may apply for a
specific permit where project-specific
review would determine mitigation
requirements.
Issue. Several commenters proposed a
conservation fund or conservation fee in
addition to any required compensatory
mitigation.
Response. The Service has numerous
authorities that allow it to charge an
entity permit fees and enter into
reimbursable agreements. Funds
collected through permit fees and
reimbursable agreements are used to
defer the cost of administering the
permit program, including, but not
limited to, salary and other staff-related
costs and costs to ensure that issuance
of permits is compatible with the
preservation of eagles. Based on
suggestions provided in public
comments and as consistent with the
use of collected fees, the Service will
use these fees to fund analysis to: (1)
better understand eagle population
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dynamics, including the risk to eagles
from authorized activities; (2) better
understand mitigation outcomes,
including researching and validating
avoidance, minimization, and
compensatory mitigation measures; and
(3) address and improve various
components of the eagle permitting
program, including gathering and
analyzing demographic data, GPS
tagging and tracking eagles for
programmatic monitoring, and
researching and validating monitoring
measures. The Service does not have
express statutory authority under the
Eagle Act to require contribution into a
conservation fund beyond these
purposes, nor the specific authority to
direct such funds if they were collected.
Changes to Fees
Issue. Multiple commenters suggested
that the fees for general permits were
too high and would disincentivize
smaller entities from participating.
Response. In the final rule, the
Service has adopted a scaled fee
approach for both general permits and
specific permits. For power lines,
general-permit administration fees are
separated into Tier 1 for non-investorowned utilities and Tier 2 for investorowned utilities (using U.S. Energy
Information Administration definitions).
For wind energy, general-permit
administration fees are separated into
Tier 1 distributed and community scale
and Tier 2 utility scale, using the
Service’s Land-Based Wind Energy
Guidelines definitions. For specific
permits, the Service created a tiered fee
structure for wind energy and power
line projects consisting of three tiers:
Tier 1, Tier 2, and Tier 2 with
reimbursable agreement, where a Tier 1
fee is charged for standard applications
and a Tier 2 fee is charged for complex
applications. A reimbursable agreement
will be used when processing time
exceeds 275 staff hours. The Service
retains the current non-commercial and
commercial tiering for disturbance and
nest take permits.
Coordination With States
Issue. Several commenters stressed
the need for the Service to coordinate
with other Federal and State agencies on
the issuance of general and specific
permits.
Response. The Service values
coordination with Tribal, State, and
Federal partners, and we intend to
continue to coordinate and share
information about permits issued. For
general permits, we will regularly be
compiling and distributing information
on general permits issued. We have
updated the regulation to reflect what
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information will be made readily
available to partners and the public. For
specific permits, the Service will
continue to consult States, Tribes, and
other Federal agencies as part of our
normal permitting procedures. In
addition, Department of the Interior
disclosure policies (68 FR 52610, Sept.
4, 2003) under the Privacy Act also
provide for routine disclosures to
Federal, Tribal, State, local, or foreign
agencies, including to exchange
information on permits granted or
denied, to ensure compliance with all
applicable permitting requirements and
obtain advice relevant to approving or
denying a permit.
Issue. Some commenters expressed
concern about the locations of eagle
nests being shared with the public,
while others stated that some States are
prohibited from disclosing nest
locations and that the Service should
not require that information on permit
applications.
Response. The Service requires
precise location information on nest
locations to properly analyze effects to
eagles, including LAP effects, as well as
for law enforcement purposes. The
Service will take all available measures
to protect eagles and their nest
locations. The Service will continue to
coordinate with State wildlife agencies
on these matters.
Issue. We received comments that
expressed concerns with the take of
eagles in States where either the bald
eagle, golden eagle, or both are listed as
threatened or endangered at the State
level. These comments requested that
the Service provide details regarding
coordination with the States with
respect to the distribution of authorized
take across individual EMUs, as well as
in relation to the quantification of LAP
thresholds.
Response. Federal issuance of a
permit does not supersede Tribal or
State protections of a species. Tribes,
States, and other Federal agencies are
not required to authorize incidental take
of bald eagles or golden eagles, even if
a permittee has obtained a Service
general or specific permit. It is the
responsibility of the permittee to ensure
they are in compliance with all
applicable laws and regulations. To
support the protection of local
populations in this rulemaking, the
Service has retained the existing
preservation standard that requires the
Service to determine that permits we
issue are consistent with eagle
preservation at the EMU and LAP
scales. Under general permits, the
Service will not analyze cumulative take
at the LAP scale prior to general permit
issuance. However, the Service will
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review general permits issued and
analyze cumulative take at the LAP
scale if an area of concern is identified.
States are encouraged to review the
Service’s issued permits and submit any
information to the Service that might
assist with assessing impacts to LAPs. If
the Service is concerned about the
status of any LAP, we can either (a)
direct compensatory mitigation to areas
of concern, or (b) suspend the generalpermit program in whole or in part.
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Definitions
Issue. The Service received comments
on the definition of ‘‘in-use nest,’’
particularly regarding determining egg
viability and nests that are considered
under construction.
Response. The purpose of this change
is to address the increasing frequency of
instances of bald eagle nest activity
outside of the breeding season,
including non-viable eggs in nests
outside of breeding season and nests
being maintained outside of breeding
season. The Service agrees with the
expressed difficulty of determining if an
egg is viable in the field. Eggs should be
assumed viable, unless evidence proves
otherwise. Evidence like the absence of
adults for several days or presence of
eggs out of breeding season should be
used to assess the likelihood of an egg
being viable. We removed the
protections for nests under construction
or under maintenance for bald eagles.
The previous definitions were part of a
conservative approach for the
recovering bald eagle that is no longer
warranted. These changes are
appropriate and improve consistency
between the Eagle Act nest protections
with the Migratory Bird Treaty Act nest
protections.
EA Alternatives
Issue. The Service should reconsider
Alternative 2 in the draft EA.
Response. The Service did reconsider
Alternative 2 and again concludes it has
a high risk of not meeting our
preservation standard if implemented.
Under Alternative 2, the regulations
would be revised to include a general
permit for land-based wind energy
facilities only, with eligibility based on
a project’s distance from eagle nests and
compensatory mitigation requirements
in the form of a flat, per-project fee for
mitigation. Adopting Alternative 2 is
problematic because neither the Service
nor project proponents know where all
eagle nests on the landscape are located.
This lack of data reduces our ability to
reliably determine whether a specific
wind project is eligible for a general
permit. This situation also adds
uncertainty for projects as well as to any
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assessment the Service might perform.
Considering this, we expect Alternative
2 would come with the highest risk of
inconsistency with our preservation
standard compared to the other
alternatives.
The Service concludes that the
general-permit program described under
Alternatives 3 and 4 will best
accomplish the dual goals of increasing
participation and increasing
conservation for eagles, where more
than 80 percent of existing turbines on
the landscape are eligible for general
permits (and the associated benefits of
those general permits) and where paths
to a streamlined issuance of specific
permits are described.
The Service also concludes that
Alternative 2’s flat fee for mitigation and
monitoring may disincentivize smaller
projects (e.g., tens of turbines) from
applying for take permits compared to
larger projects (e.g., hundreds of
turbines). The Service estimates that an
average wind project qualifying for a
general permit will pay $312,000 in
compensatory mitigation under
Alternative 2. This is nearly ten times
the estimated compensatory mitigation
cost of $37,200 for Alternatives 3 and 4.
Although industry trends may be
toward new construction of larger
facilities and consolidated ownership,
wind energy facilities are long lived
(usually 30 years or more). Older
facilities will continue to operate and
must be considered when estimating
participation in eagle incidental-take
permitting and when considering
financial impacts to permittees under
Alternative 2 (Section 5.4.5.1 of the
Environmental Assessment). Although
risk to eagles from small facilities that
are eligible for general permits may be
relatively low, under Alternative 2,
those businesses would be more
susceptible to future enforcement
actions and associated enforcement
costs in the event of an eagle take if they
remain unpermitted due to the
relatively high cost of flat fees.
EA Economic Analysis
Issue. The Service received several
comments on our estimated mitigation
costs, with some commenters suggesting
our estimates were too high while others
suggested they were too low.
Response. Because compensatory
mitigation is provided either by the
permittee or a third party, costs can vary
widely. We acknowledge that the costs
estimated for compensatory mitigation
under all alternatives in the FEA are
estimates and are likely to vary, perhaps
substantially, across all permitted
projects based on the mitigation method
selected, the in-lieu fee program or
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conservation bank selected, and other
details. These details are difficult to
account for in an economic analysis, but
we considered them as accurately as
possible based on current data and our
estimated projections. In the FEA, the
Service estimates compensatory
mitigation for an average wind energy
general permit to be $37,200. These
estimates are based solely on estimates
of compensatory-mitigation costs using
power pole retrofits, which are the only
cost estimates the Service currently has
available.
Issue. The Service received comments
specifically on our cost estimates for
retrofitting power poles under the
power line regulation.
Response. We updated the FEA to
reflect our assumption that the proactive
retrofit requirements associated with
this rule are not expected to result in
additional costs to power line entities.
As stated in section 5.6.5 of the FEA, the
Service assumes that power line entities
most likely to apply for a permit are
entities that have a risk of taking eagles
and are already retrofitting power poles,
thus already meeting this requirement.
Eligibility—Wind Energy General Permit
Issue. Many commenters expressed
concerns with the general-permit
eligibility for wind energy, specifically
regarding the distance from bald eagle
nests.
Response. The Service acknowledges
the uncertainty that is created if bald
eagles initiate nesting near a project
with a wind energy general permit.
Therefore, we revised eligibility criteria
(§ 22.250(c)) to provide that a general
permittee remains eligible to renew
their permit, even if the Service revises
eagle relative abundance thresholds or
eagles construct nests within the
species-specific setback distances, as
long as the project does not discover the
remains of four eagles of the same
species within a 5-year permit tenure.
Issue. Multiple comments requested
that the Service create a general permit
option for existing wind energy projects
(as defined in § 22.250(b)) occurring
within the specific permit zone.
Response. The Service acknowledges
the unique challenges of existing
projects being subject to new
regulations. However, after extensive
review, the Service could not identify a
set of general-permit eligibility criteria
that a project could self-certify without
adding extensive complexity or
uncertainty. Therefore, the Service
retained and clarified the eligibility
criterion that any existing project that
does not meet general permit eligibility
criteria can apply for a specific permit
(§ 22.200(b)(7) while requesting a letter
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of authorization to obtain a general
permit (§ 22.250(c)).
The Service will review all
information provided in the application,
including any site-specific, preconstruction or post-construction data.
If we determine that the take rates at the
existing project are likely to be
consistent with or lower than eagle take
rates expected at similar-sized wind
facilities that qualify for general
permits, the Service will issue a letter of
authorization to register for a general
permit. If an applicant receives a letter
of authorization, we may refund the
specific permit application fee, but to
cover the cost of review, we will not
refund the administration fee. The letter
of authorization may require additional
avoidance, minimization, or
compensatory mitigation requirements
as needed to ensure consistency with
general permit take rates. The Service
anticipates expediting the processing of
these applications.
Issue. Commenters suggested that the
Service should allow the use of sitespecific data to determine eligibility for
general permits.
Response. The Service recognizes the
value in site-specific data. However, the
purpose of general permits is to apply
an efficient and streamlined approach
for issuing permits to projects that the
Service can pre-determine pose
relatively low risk to eagles. It is not
currently possible to evaluate sitespecific data in an automated manner,
which is necessary for general permits.
Applicants that prefer to use sitespecific data may apply for a specific
permit and request review for inclusion
in the general-permit program as
described in a previous comment
response.
Issue. Commenters suggested that
existing projects should still qualify for
a general permit even if some of the
project’s turbines are within the specific
permit zone.
Response. The Service reviewed at
length the possibility of automatically
allowing general-permit eligibility for
projects that overlap the boundaries
between specific and general permit
zones. This deviation from the proposed
rule appears simple but comes with an
increased risk that our general permit
program would be inconsistent with the
preservation standard established by the
Eagle Act and implementing
regulations. The risk is further increased
because the projects that would be
eligible for general permits by partially
overlapping the general-permit zone
would very likely create higher risk to
eagles than other projects that fully
encompass the general-permit zone. The
Service must choose between
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addressing that risk by increasing the
mitigation costs for all general
permittees or retaining that all turbines
must be in the general permit zone.
Because of how substantive the
increased mitigation costs were, the
Service instead provides a mechanism
for existing projects to request an
eligibility determination case-by-case as
described in a previous comment
response.
Issue. Comments noted that many
existing projects would not qualify for a
general permit and stated that many of
the current deficiencies with the
specific permit program would still be
present under the new regulations.
Response. The Service has developed
and will implement a streamlined
approach to specific permits. One
approach we considered and adopted in
the final rule was the creation of new
tiers for reviewing specific-permit
applications. The purpose of these tiers
is to separate the specific-permit
applications that are able to adopt
standardized approaches from those
which request more extensive review
and negotiation. Applicants that are
willing to accept standard specificpermit conditions (and do not require
additional NEPA analysis) are eligible
for a less expensive application fee and
faster permit-review times.
Eligibility—Relative Abundance Map
and Thresholds
Issue. Comments suggested that the
relative abundance maps should
indicate levels of risk so developers
could choose to avoid the highest risk
areas, or, at a minimum, understand
increased mitigation costs that might be
associated with higher risk areas.
Response. The map published with
the final rule uses eagle relative
abundance as an index for potential
risk. We use relative abundance data for
eagles because the presence of more
eagles in a given area at different times
of the year results in more interactions
between turbines and eagles and
therefore increased risk of collisions.
Thus, relative abundance data is an
effective proxy for determining the risk
of eagle take in a particular location.
Although there are only two levels of
risk depicted in this map, it does
highlight areas that the Service has
deemed to have relatively high or
relatively uncertain risk to eagles. It is
our intent that this map will be used by
developers when siting wind-related
infrastructure. As additional data
become available, we will continue to
refine our ‘‘risk maps.’’
Issue. The Service received numerous
comments regarding the use of eBird
Status and Trends relative abundance
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products to create the relative
abundance map. Some commenters
expressed concern that use of eBird data
would underestimate eagle abundance
in areas inaccessible to birders.
Response. The Service recognized that
data products from the Cornell Lab of
Ornithology using eBird data is new to
many. It is important to distinguish that
the data products the Service is using
are distinct from raw eBird data. We
consider the products from the Cornell
Lab of Ornithology to be currently the
best available science for developing a
nationwide approach to permitting. We
recognize and acknowledge the
uncertainties that are included with this
method, such as areas where raw eBird
data has limited reporting. However, the
Cornell Lab of Ornithology eBird Status
and Trends relative abundance products
use machine learning to fill in these
gaps based on the models’ ability to
relate the eBird observations to
environmental predictors derived from
global remote sensing data. For
example, reliability of species
distribution model predictions can be
increased for unsampled locations and
times by relating environmental
predictors to observed occurrences or
abundances. This approach allows us to
predict abundance in places that may
not be frequented as often (or at all) by
eBird users.
Issue. Several comments suggested we
use information from other datasets
(e.g., migration counts, telemetry
studies, roost registries, USGS breeding
bird survey, Audubon Christmas Bird
Count, and the Midwinter Bald Eagle
Survey) to supplement and improve
maps either in addition to or as part of
the eBird models.
Response. The Service agrees that the
best information should be used to
determine eagle relative abundance. To
implement general permits, the Service
must regulate at the national scale,
which is why this regulation relies on
data products from the Cornell Lab of
Ornithology. The Service intends to
incorporate other data into our mapping
efforts, as appropriate. However, it will
take time to review each dataset,
including its assumptions and biases,
and incorporate those data into mapping
efforts in a meaningful way and at
appropriate scales. We welcome
additional information and data that
could help with risk mapping and any
investment in data integration efforts.
Issue. We received comments
requesting that the Service further
stratify relative abundance thresholds
according to differences in geography
(e.g., northern and southern for bald
eagles and eastern and western for
golden eagles).
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Response. The Service considered
further stratification and the creation of
separate relative abundance criteria for
each eagle species preceding the public
comment period. However, adding
additional strata would have changed
the scale at which the relative
abundance is evaluated and would have
added significant complexity to the
general permit program for wind energy
facilities. Thus, we elected not to
incorporate these changes.
The Service will update the map and
relative abundance thresholds
periodically. In the FEA, we suggested
every 5 years or different intervals if
information suggests shorter or longer
intervals are more appropriate. Between
updates, the Service will consider any
suggestions for better and more effective
ways to map relative eagle abundance.
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General Permits
Issue. One commenter indicated that
they thought the proposed rule placed
too much emphasis on general permits.
Previously, all eagle take was permitted
with specific permits.
Response. This rule emphasizes
general permits because that is the
provision that is being introduced with
this rulemaking. The Service has
retained the specific permit approach
and provisions. In this rulemaking, the
Service has created general permits as
an alternative approach to obtaining
eagle take authorization for projects that
meet eligibility criteria. The purpose of
general permits is to simplify and
expedite the permitting process for
activities for which the Service has
well-established avoidance and
minimization measures and that have
relatively consistent and low risk to
eagles. The regulations are based on the
well-established avoidance,
minimization, and compensatory
mitigation measures that the Service has
been implementing as permit conditions
for the past 14 years. This approach
allows us to confidently authorize take
consistent with the preservation
standard established by the Eagle Act
and implementing regulations without
requiring Service review prior to
issuance. We will continue to refine the
general permit approach and
incorporate public input on eligibility
criteria for all general-permit categories
included in this rule to ensure that
general permits effectively simplify and
expedite the permit process for eligible
projects while meeting the preservation
standard.
Issue. Many comments recommended
that the Service allow project
proponents to apply for a separate
permit for bald and golden eagles, as
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opposed to requiring coverage for both
species.
Response. In reviewing comments, the
Service realized we did not sufficiently
explain in the proposed rule that the
mitigation requirements are specific to
that EMU and proportional to golden
eagle abundance in the EMU.
Commenters expressed concern that
projects in the East, where golden eagle
use of wind projects is seasonal and
generally relatively low, would be
paying to compensate for authorized
golden eagle take in the West, where
golden eagle use of wind projects can be
relatively high. This is not the case.
Projects in the Atlantic and Mississippi
EMU have a lower golden eagle
mitigation rate that is commensurate
with the generally lower risk of golden
eagle take in those EMUs. Similarly,
projects in the Central and Pacific EMUs
will be required to pay a higher
compensatory mitigation rate for golden
eagles, commensurate with the generally
higher risk of golden eagle take there.
There is a small amount of additional
mitigation required in all EMUs, to
provide funds if a LAP threshold is
exceeded and mitigation is necessary for
the program to remain consistent with
our preservation standard. These details
are covered in the Final Environmental
Assessment associated with this
rulemaking.
Between the proposed and final rule,
the Service again analyzed the
possibility of authorizing general
permits by species and did not select
that approach at this time. While
seemingly a straightforward request,
separating the species introduces
uncertainty, which increases the risk
and complexity of general permits. To
meet the preservation standard, the
Service estimates general permit
mitigation requirements based on
enrollment and has no basis for
predicting how many projects will opt
for coverage of one species versus both.
The Service would effectively need to
develop separate general permits for
each species, including corresponding
eligibility thresholds, eligibility maps,
mitigation costs, and perhaps
monitoring standards. In the interest of
keeping general permits easy to apply
for and implement, the Service retained
the requirement that all general permits
authorize take of both eagle species. The
Service will continue to review this
approach in future rulemaking.
To illustrate the mitigation costs that
will be required under general permits
and how they differ across project sizes
and across EMUs, consider two
hypothetical projects: one with 30 and
one with 100 project turbines, all
turbines having a 95.7m rotor diameter.
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9935
Both projects are eligible for a general
permit and are located in the Atlantic/
Mississippi EMU (where general permit
mitigation rates for golden eagles are the
lowest). We will also consider those
same two projects as being eligible for
general permits in the Pacific EMU
(where general permit mitigation rates
for golden eagles are the highest). The
30-turbine project in the Atlantic/
Mississippi EMU would be required to
mitigate for 0.20 golden eagles and 0.06
additional eagles (LAP mitigation), or
0.26 total eagles, every 5 years. That
same project in the Pacific EMU would
be required to mitigate for the take of
0.42 golden eagles and 0.06 additional
eagles (LAP mitigation), or 0.48 total
eagles, every 5 years. The 100-turbine
project in the Atlantic/Mississippi EMU
would be required to mitigate for 0.66
golden eagles and 0.20 additional eagles
(LAP mitigation), or 0.86 total eagles
every 5 years. That same 100-turbine
project in the Pacific EMU would be
required to mitigate for 1.40 golden
eagles and 0.20 additional eagles (LAP
mitigation), or 1.60 total eagles every 5
years.
These two hypothetical projects
illustrate the relatively low cost of
obtaining golden eagle take coverage for
projects that are eligible for a general
permit, and especially the lower cost for
smaller projects and projects in the East,
where golden eagle presence is seasonal
and they are generally less abundant
than in many parts of the West. We are
hopeful that general permit applicants
who think their risk to golden eagles is
low will view this relatively low
mitigation cost as worth the price of
incidental take authorization for golden
eagles, in the event such take should
occur. If applicants wish to receive a
permit for only one eagle species, they
may apply for a specific permit.
Issue. Several comments expressed
concern with regard to potential
suspension or termination of the general
permit program, including a suggestion
that suspension or termination should
be subject to public notice and comment
prior to finalization.
Response. The Service recognizes the
uncertainty that a potential suspension
or termination causes. Suspension or
termination of general permitting is an
important aspect to allow the Service to
respond quickly in the event of sudden
changes in eagle populations at the LAP
or EMU scale; however, it is not a step
the Service would take lightly and
without a notice and comment process.
Regulations currently allow for the
revocation of a permit if ‘‘the
population(s) of the wildlife or plant
that is the subject of the permit declines
to the extent that continuation of the
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permitted activity would be detrimental
to maintenance or recovery of the
affected population’’ (50 CFR
13.28(a)(5)). The Service will regularly
evaluate whether the authorized take of
bald eagles and golden eagles under
general permits remains compatible
with the preservation of eagles. If the
Service finds that issuance of general
permits in a particular LAP or EMU is
not compatible with the preservation of
bald eagles or golden eagles, we would
first consider adding additional
precautions to the permitting program
through rulemaking. Rulemaking
requires public review and comment
periods. However, the Service is
preserving, as a last resort, the option of
suspending general permit issuance
locally or nationally after publishing a
notice in the Federal Register. This
notice may include an opportunity for
the public to comment on next steps. If
the Service suspends general permitting,
take currently authorized under a
general permit remains authorized until
expiration of that permit, unless the
permittee is notified otherwise.
Issue. Some commenters asked us to
explain how ‘‘low effects’’ are
determined for general permits.
Response. Public comment indicated
that the Service’s intent was not clear in
the usage of the phrase ‘‘low effects.’’
We have modified the text to instead
reference ‘‘low risk.’’ General permits
simplify and expedite the permitting
process for activities that have relatively
consistent and low risk to eagles and
well-established avoidance,
minimization, and compensatory
mitigation measures. For wind energy
facilities, projects that have low risk
will be determined by the relative
abundance of eagles and the proximity
of wind turbines to nest locations. For
other general permits, the Service
considers the implementation of the
well-established avoidance and
minimization measures to result in
those projects being low risk to eagles.
Guidance
Issue. Several commenters requested
more information regarding guidance
documents that the Service plans to
develop.
Response. The Service is working on
internal procedures, external outreach,
and guidance documents to help the
public understand and comply with
these new regulations. In developing
guidance, the Service will follow
standard Federal guidance practices. All
regulatory requirements are included in
the rule. Guidance documents provide a
step-down from the rule that explain
and clarify the Service’s expectations on
how to meet regulatory requirements.
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Monitoring
Issue. While many commenters were
supportive of the removal of third-party
monitoring, we received comments in
support of retaining this provision.
Response. The third-party monitoring
requirement has proven impracticable
or impossible to implement at some
projects for a variety of factors,
including health, safety, liability, and
access issues for project sites that are
leased from multiple private
landowners. These factors have created
a barrier to obtaining a permit. The
Service reviewed the purpose of thirdparty monitoring and determined in
most circumstances it is sufficient to
rely on the requirement that the
permittee must certify that the
information submitted is complete and
accurate to the best of their knowledge
and belief, subject to criminal penalty
for supplying false information. The
Service concluded that the existing
penalties for false reporting under eagle
take permits will be enough to dissuade
most permittees from intentionally
providing inaccurate reports. We retain
the ability to require third-party
monitoring on a case-by-case basis for
specific permits, particularly if we have
ongoing compliance concerns.
Issue. Commenters expressed concern
over the amount of money the Service
was proposing to spend on monitoring.
Response. The Service recognizes the
tradeoff between spending money on
monitoring or on compensatory
mitigation. Monitoring can be
expensive, and it may not be
immediately clear how more monitoring
benefits eagle preservation. The benefit
of compensatory mitigation is more
straightforward. While extensive
monitoring has occurred at numerous
wind projects, it remains difficult to
draw programmatic, cross-project
conclusions. Monitoring in a manner
that allows for programmatic
conclusions is critical to ensure
implementing these new regulations
will be compatible with eagle
preservation.
However, based on public comment,
the Service reviewed its proposed
approach to monitoring. We determined
that we can accomplish monitoring
goals under general permits with
concurrent fatality monitoring, which
will be required under general permits,
and without additional monitoring
performed by or contracted by the
Service. In the final rule, we require
concurrent monitoring conducted
according to Service protocols by
project operations and maintenance
staff, which will be sufficient to meet
the Service’s monitoring needs,
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provided there is sufficient participation
in wind energy general permitting. We
continue to require an administration
fee, a portion of which will be used to
validate the concurrent monitoring
approach and analyze monitoring data.
Issue. We received comments that
expressed concern over the removal of
the required 5-year check-ins.
Response. The purpose of 5-year
review is to update take estimates and
related compensatory mitigation for the
subsequent 5-year period. It also
provides the Service with an
opportunity to amend the permit to
reduce or eliminate conservation
measures or other permit conditions
that prove to be ineffective or
unnecessary. The purpose of these
reviews does not change with this
rulemaking. However, the 5-year
requirement has introduced unintended
uncertainty which, according to public
comment, has reduced participation in
eagle take permitting under the 2016
regulations. It has also resulted in
timing issues, where post-construction
monitoring or other data is available offcycle from the 5-year timing (e.g., year
3 or 4) but cannot be used until the
scheduled check-in. Instead, check-ins
may now be initiated by the permittee
or the Service in response to events that
warrant review, for example, updating
fatality estimates and associated
compensatory mitigation requirements
or revising permit conditions to reflect
the best available science.
Issue. We received comments stating
that our current surveys are not
sufficient to adequately estimate eagle
population numbers and that mortality
data reporting is voluntary and
unreliable.
Response. The Service uses the best
available science in ensuring that
general and specific permits are
consistent with the preservation of
eagles. The Service has conducted aerial
surveys for both bald eagles and golden
eagles relatively recently and consider
these survey efforts adequate to estimate
populations of both species within
applicable parts of their range. The
Service agrees that voluntary reporting
of mortality data is unreliable. With this
rulemaking, the Service improves
voluntary reporting at wind projects in
two ways. First, through increasing
participation in permitting and
prescribing the concurrent monitoring
protocol all projects use, the Service
expects improved quantity and quality
of eagle fatality data at wind projects.
Second, through the collection of an
administration fee, the Service can
direct funds as needed to ensure
permitting is consistent with the
preservation standard, including by
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survey populations and by analyzing
project-specific mortality data.
Issue. Commenters felt that
monitoring related to disturbance take
and nest take should not be required,
specifically in instances where the
activity does not directly take eagles, as
with communication towers.
Response. Unlike permits that
authorize the incidental injury or death
of eagles, monitoring required under
nest take and nest disturbance permits
is intended to detect breeding outcomes
during current and subsequent nesting
attempts and, if appropriate and
practical, document if eagles breed
again at their original or any new
nesting location. The loss of breeding
productivity constitutes take, as it
prevents eagles from being added to the
population. Monitoring requirements
allow the Service to more accurately
account for authorized take against our
established species-specific take limits
and, over time, may allow us to qualify
or quantify the effectiveness of permit
conditions.
Nest Disturbance
Issue. Comments regarding nest
disturbance primarily focused on the
buffer distances set for general permits,
including those for in-use and alternate
nests, and advocated for distances based
on the level of tolerance to disturbance.
Response. By specifying distances in
our bald eagle nest disturbance general
permit, we are not suggesting that all
activities within these distances must
apply for a permit. Rather, we are
setting a standard that only those
activities listed within the final rule
(§ 22.280(b)) within these distances can
receive a general permit. This standard
is intended to prevent project
proponents applying for unnecessary
permits for activities beyond these
distances that are unlikely to disturb
breeding bald eagles. Further, the
specific and general permits for nest
disturbance are not a prerequisite to
carrying out activities or starting
projects. Instead, they cover any
disturbance that may result as an
unintentional consequence of an
activity. If an individual or entity
assesses that their activities are unlikely
to disturb breeding eagles, they do not
need the Service’s consent or
concurrence to proceed, though they
may be held liable if their activities do
ultimately cause disturbance.
The Service acknowledges the
growing body of evidence
demonstrating that some portions of the
bald eagle breeding population
demonstrate increased tolerance to
human activities. Our standards under
the nest disturbance general permit
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reflect this consideration. We use the
330- and 660-foot distances for bald
eagles because we are generally
unconcerned with activities beyond
these ranges, and we discourage
proponents from applying for permits
where best available science suggests
they are unnecessary. Within those
distances, project proponents may
assess their relative risk to eagles (e.g.,
whether or not a similar activity is or
has occurred closer to the nest) and
determine whether or not to apply for a
permit.
Regarding alternate nests, we agree
that, by definition, activities at these
nests cannot expose breeding eagles to
sensory disturbance, as the eagles are
not present. However, as the National
Bald Eagle Management Guidelines
(2007) note, alterations to the nest site
and surrounding habitat may discourage
eagles from breeding when encountered
by eagles returning to that nest site. We
will continue to update the National
Bald Eagle Management Guidelines as
well as develop similar guidelines for
golden eagles.
Issue. We received requests for a
regulatory authorization for State
wildlife agencies for land-management
activities that may improve eaglenesting habitat, including prescribed
fire and mowing.
Response. The Service acknowledges
the usefulness of regulatory
authorizations; however, we do not
consider regulatory authorizations an
appropriate mechanism to authorize the
mortality or injury of bald eagles or
golden eagles at this time. Most landmanagement activities, such as
alteration of shorelines, alteration of
vegetation, and prescribed burns, are
eligible for general permits for eagle
disturbance take. General permits for
disturbance caused by agriculture,
mining, and oil and gas operations are
not available at this time. We have
received permit requests for these
activities infrequently, thus we have not
yet developed standard avoidance and
minimization measures. Operators of
these and other activities may apply for
specific permits. As we gain more
information on the effects of these
activities and identify effective
avoidance and minimization measures,
we may in future rulemakings add
general-permit regulations for these and
other activities.
Issue. Commenters asked whether a
single general permit authorizes several
types of disturbance or whether a
separate general permit will be needed
for each type of disturbance that could
occur.
Response. Consistent with our current
approach to permitting, a single permit
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for disturbance of bald eagle nests can
authorize disturbance of a nest from
multiple sources of disturbance of a
single project or operation. For example,
a general permit could authorize
disturbance from land clearing, external
construction, blasting, and operations
and management activities associated
with one project. The bald eagle nest
disturbance permit is a ‘‘one permit, one
nesting territory’’ system that simplifies
our bald eagle population management
tracking and reduces the amount of
monitoring we require from permittees.
Issue. Commenters also expressed the
desire for one permit for all bald eagle
disturbance associated with a given
activity for the 5-year permit term.
Response. Allowing coverage for an
unspecified number of nests and ad hoc
accounting of effects would hinder our
ability to ensure take is consistent with
the preservation standard established by
the Eagle Act and implementing
regulations. Individuals or entities that
want to obtain coverage for disturbance
of multiple nesting territories may apply
for a specific permit.
Nest Take
Issue. Comments related to nest take
centered on the creation of general
permits and the lack of Service review
of those permits.
Response. General permits are
generally limited to three scenarios:
emergency circumstances, health and
human safety concerns, or nests on
human-engineered structures. These
situations, such as wildfire hazard and
structural failure, often pose risks to
both the nest and for people. In these
situations, it is often imperative that the
permit be issued as quickly as possible,
as doing so often reduces the risk or
effects to eagles. The Service also has
been implementing permits for these
activities since 2009 and has welldeveloped permit conditions with
avoidance and minimization measures.
The expedient processing and
standardized approach make these
permits a great fit for general permits.
The Service will review these permits.
In reviewing bald eagle nest take
permits at the program scale, given the
current and expected number of permits
issued and the status of the bald eagle,
the Service is confident that issuance is
consistent with the preservation of the
bald eagle. We will continue to review
nest take at the program scale to ensure
that general permit issuance is
consistent with the preservation of bald
eagles. The Service will also audit a
percentage of nest take permits, to
ensure that the applicants meet
eligibility criteria and comply with
permit conditions. We will work to
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address any compliance concerns with
individual permittees.
Issue. Some commenters requested
that a single general permit for nest take
authorize the take of multiple nests from
a single project or across a defined area.
Response. Issuing one general permit
for each nest allows the Service to
efficiently track take. If the Service
allowed coverage for an unspecified
number of nests, the associated ad-hoc
accounting of effects would make it
much more difficult for the Service to
ensure authorized take is consist with
the preservation standard. Specific
permits remain available for the take of
multiple nests.
Issue. One commenter stated that the
proposed regulation would no longer
require the Service to make a finding of
net benefit to eagles for nest take
authorized under ‘‘other purposes.’’ The
commenter interpreted the proposed
rule to state that compensatory
mitigation is required only when the
take exceeds the limit of the applicable
EMU.
Response. Since 2009, the regulations
require the finding of a net benefit to
eagles for nest take authorized under
‘‘other purposes.’’ For all nest-take
requests outside of Alaska, a specific
permit is required for the purposes of
the Service determining whether a net
benefit will be achieved by the proposed
action, or, if the activity does not
provide the net benefit, the
compensatory mitigation proposal. The
net benefit to eagles is scaled to the
effects of the nest removal. The Service
did include a general permit for ‘‘other
purposes’’ in Alaska because of the
scaled effects of nest removal. In Alaska,
well-established permit conditions
provide sufficient avoidance,
minimization, and compensatory
mitigation scaled to the effects of nest
removal, given the robust population
status of the bald eagle and the available
nesting habitat.
Issue. Some entities expressed
support for the creation of general
permits for golden eagle nest take.
Response. The Service did not
include but will continue to work to
develop general permits for golden eagle
nest take. The Service has issued few
golden-eagle nest take permits and
therefore does not have sufficient, wellestablished measures to create general
conditions for golden eagle nest take.
Issue. One commenter suggested that
authorizing the take of eagle nests to
protect threatened or endangered
species should apply only to bald eagles
due to the golden eagle’s population
status.
Response. With expanding bald eagle
populations, the Service foresees
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situations arising where the take of an
eagle nest may be necessary for the
recovery of threatened or endangered
species. However, the Service
acknowledges the tradeoffs are more
complex with golden eagles. Because
this is an emerging issue, a specific
permit must be obtained for this type of
activity. The Service added an
additional precaution in that the
Federal, State, or Tribal agency
responsible for the species of concern
must obtain the permit. The Service will
assess the tradeoffs between the eagle
species taken and the endangered or
threatened species. The Service will
consider the evidence that eagles are
limiting the recovery of a threatened or
endangered species and analyze
whether the eagle nest removal will
improve recovery for the threatened or
endangered species in question. The
Service will consider if issuing this
permit, including required avoidance
and minimization measures and
compensatory mitigation, is consistent
with our preservation standard at both
the LAP and EMU scale. Finally, the
Service will consider if other methods
are feasible that have less effect on
eagles but will still abate or prevent the
problem. As a final protection for
golden eagles, the Service may require
compensatory mitigation for the take of
golden eagle nests.
Permit Conditions
Issue. Commenters asked whether the
provisions in the new rule would apply
to entities that currently have long-term
incidental take permits and entities that
applied but have yet to receive a permit.
Response. Projects that have
submitted an application as of February
12, 2024, will have until August 12,
2024, to choose whether to have their
application reviewed and administered
under all the provisions of the 2016
regulations or all the provisions of these
new regulations. Projects permitted
under the 2016 regulations may
continue under existing permit
conditions until the permit expires.
Permittees that want to modify existing
permit conditions to comply with the
new regulations may contact their
permitting office at any time to
determine whether a substantive
amendment request or a new
application is most appropriate. For
qualifying projects that elect to have
their pending applications reviewed and
administered under all the provisions of
these new regulations, application fees
paid prior to August 12, 2024, may be
used to pay for application and
administration fees required under the
new regulations.
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Issue. Multiple commenters expressed
concerns over operations and
maintenance staff conducting
monitoring, suggesting that they might
underreport their findings or that they
would find too few available carcasses
to provide useful information on eagle
take.
Response. There are two aspects to
this concern. The Service acknowledges
the concern about staff intentionally
underreporting their findings. Based on
input the Service received, we predict
this will be a rare circumstance and one
that can be discovered and addressed
with the assistance of the Office of Law
Enforcement. With any permit, there
will be good actors and bad actors, and
the Service will address bad actors
accordingly.
For the second aspect, the Service
disagrees that concurrent monitoring
will not provide useful information.
Service analysis suggests that, on a large
scale (e.g., aggregation of all general
permits), concurrent monitoring will
provide sufficient information over time
to allow the Service to be confident that
our resulting program-wide take
estimates are consistent with the
preservation of eagles.
Issue. A commenter requested
clarification as to when an adaptive
management plan is required.
Response. It is expected that wind
energy project proponents will develop
an adaptive management plan prior to
or on obtaining a general permit.
However, implementation of the
adaptive management plan is required
only if a certain number of fatalities are
discovered at a wind energy facility. If
three bald eagle injuries or mortalities,
or three golden eagle injuries or
mortalities, are discovered at a project
during the 5-year general permit tenure,
the permittee must provide the Service
with an adaptive management plan and
specify which avoidance and
minimization measures the permittee
will implement. If an injury or mortality
of a fourth eagle of that species
attributable to the project is discovered,
the permittee must identify and
implement the avoidance and
minimization measures outlined in the
adaptive management plan. Adaptive
management plans may be revised
during the permit tenure. A copy of
adaptive management plan(s) may be
requested by the Service at any time as
part of an audit.
Issue. One commenter asked for
clarification whether circumstances
impacting eagles outside of a specific
permittee’s control (e.g., decrease or
shift in population due to disease,
climatic factors, or illegal take like
poisoning and poaching) could result in
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new obligations being imposed on a
specific permit holder.
Response. Circumstances outside the
permittee’s and the Service’s control
will continue to affect eagle
populations. The permittee’s
responsibility is to comply with the
requirements of their permit. The
Service’s responsibility is to ensure
permits issued are consistent with the
preservation of eagles, including at the
EMU and LAP scales. If situations arise
at the EMU and LAP scale that are
detrimental to eagle populations, the
Service may need to act to ensure
preservation of eagles, which may
include programmatic changes to
permits or changes to a subset of
permits. Generally, we will first attempt
to address these issues modifying the
requirements for or restricting new
permits. However, consistent with 50
CFR 13.23(b), the Service reserves the
right to amend any permit for just cause
at any time during its term, upon
written finding of necessity.
Power Lines
Issue. Comments regarding eagle
incidental take permits for power lines
were focused primarily on the required
conditions and definitions in the
regulation.
Response. The Service made several
improvements to the power line
regulation:
1. To better align with standard
industry terminology, the Service
revised the term ‘‘electrocution-safe’’ to
‘‘avian-safe.’’
2. The Service clarified that power
line entities are required to ensure that
all poles constructed in high-risk eagle
areas are avian-safe, allowing the entity
to determine those areas within the
parameters provided by Service
guidance.
3. To address concerns regarding the
siting of projects and buffer distances,
we revised the conditions to read as
follows: ‘‘For new construction and
rebuild projects, reconstruction, or
replacement projects, incorporate
information on eagles into siting and
design considerations. Minimize eagle
risk by siting away from eagle use areas
(e.g., nests and winter roosts),
accounting for the risk to and
population status of the species, unless
this requirement would unduly impact
human health and safety; require overly
burdensome engineering; or have
significant adverse effects on biological,
cultural, or historical resources.’’
4. The Service modified the definition
of ‘‘collision response strategy’’ to
reflect that any risk-reduction strategies
implemented post-collision should be
commensurate with the collision risk.
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This may include no changes for one-off
situations that are unlikely to reoccur.
References to changes in engineering
design have been removed and will
instead be included in guidance.
5. Many companies were concerned
that the proactive retrofit strategy would
be infeasible to implement. Proactive
retrofit strategies are important, as they
serve as the compensatory mitigation
requirement for power line entities.
However, the Service also wants to
ensure that requirements are feasible.
The Service modified the requirement to
a 50-year strategy for investor-owned
utilities and a 75-year strategy for noninvestor-owned utilities, with 5-year
benchmarks. We also clarified that this
requirement applies only to poles in
high-risk eagle areas that are not aviansafe but may include other poles in the
service area as well. The Service
provides for delayed implementation to
allow utilities to develop proactive
retrofit strategies. The Service also
provides for extenuating circumstances,
such as catastrophic weather, wildfire,
or other events that substantively
disrupt power delivery, in
implementing these strategies. Finally,
we note that specific permits are
available for any utility that is unable to
implement the general permit
requirements.
6. The Service amended the
conditions associated with the reactive
retrofit strategy to clarify that the
evaluation of the incident must be
completed within 90 days and the
response implemented within 1 year of
the incident.
7. The Service clarified that the
minimum expectation for the eagle
shooting response strategy is for utilities
to notify the Office of Law Enforcement
in the case of a confirmed or suspected
shooting. However, we will work with
industry to develop other commonsense response options.
Issue. Several comments expressed
concerns regarding the costs associated
with implementing the avoidance and
minimization measures for power lines.
Response. The fees and costs to
applicants to participate in the
permitting framework have been
updated and are included in the FEA.
See tables 5–1 (No Action Alternative),
5–4 (Alternative 2), 5–10 (Alternative 3),
and 5–14 (Alternative 4). These tables
comprise all fees and costs that a
permittee is expected to accrue in
applying for and complying with all
permits. As stated in section 5.6.5 of the
FEA, the Service assumes that power
line entities most likely to apply for a
permit are entities that have a risk of
taking eagles and are already retrofitting
power poles, thus already meeting this
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9939
requirement. Therefore, the Service does
not anticipate an added cost to power
line entities for the retrofit requirement.
Specific Permits
Issue. Several commenters expressed
concerns with delays in specific permit
issuance review and requested that the
Service further streamline the specific
permit process.
Response. The Service will be
implementing several approaches to
improve efficiency in the specific
permit process. One approach codified
in this rulemaking is the creation of new
tiers for reviewing specific permit
applications. These tiers separate the
specific permit applications that require
extensive review and negotiation from
those that do not, creating a streamlined
approach and corresponding reduced
application fee for projects that meet the
new Tier-1 criteria.
In addition to creating a tiered
approach allowing faster processing for
Tier-1 specific permits, the Service will
institute a procedural change to further
expedite review of some projects. To
date, 42 eagle incidental take permits
have been issued to wind energy
projects across the country. While all
permit decisions were analyzed in an
EA or, occasionally, an EIS, our
experience with issuing these permits
has led us to conclude that a categorical
exclusion would be appropriate for most
permit decisions because relevant
environmental impacts for most
decisions have already been analyzed in
the 2016 PEIS and extraordinary
circumstances are unlikely to apply,
given the general impacts we disclosed
in our NEPA analyses for previously
analyzed decisions. Specific permit
decisions we expect to categorically
exclude from further NEPA analysis
must, at a minimum, include the
following criteria: (1) Estimated annual
eagle take, after compensatory
mitigation (if required), is below EMU
take limits; (2) estimated annual eagle
take, combined with other authorized
take in the vicinity, does not exceed five
percent of the project-specific Local
Area Population; (3) permit conditions
do not have the potential to cause
effects on cultural resources or other
historic properties protected by the
National Historic Preservation Act; (4)
permit issuance will not be precedent
setting; (5) the permit decision and
permit conditions will not be based on
take estimates produced from new or
unpublished methods or models; and (6)
no other extraordinary circumstances
that prevent application of the
categorical exclusion exist. If the
Service determines categorical
exclusion is not appropriate, the Service
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will initiate an EA or EIS in accordance
with NEPA. To ensure linear and
efficient progress, substantive Service
work on these documents will begin
after the applicant and the Service have
completed negotiations on the
conditions of the permit.
Tribal Concerns
Issue. There were concerns expressed
regarding the removal of protections
from § 22.85 of the existing regulations,
including the following:
• Evaluation of cultural significance
of a local eagle population;
• Finding of a practicable alternative
to nest removal;
• Finding of a net benefit to eagles
and subsequent compensatory
mitigation;
• Determination of whether suitable
nesting and foraging habitat is available
to accommodate eagles displaced by
nest removal; and
• Finding that permits will not
preclude higher priorities, including
Native American Tribal religious use.
Response. The Service did not intend
to remove the protections listed above.
Many were moved to other sections or
condensed with other regulatory
language with the intent to provide
clarity. However, comments indicate
this rearrangement did not improve
clarity. We have re-expanded the
regulatory language or relocated the
language to the expected locations.
Issue. Several comments from Tribes
focused on the creation of general
permits, particularly for nest take and
nest disturbance.
Response. Regarding opposition to
general permits for nest take and nest
disturbance, the Service notes that these
permits are only for emergencies, for
health and safety issues, or on humanengineered structures. In most cases,
these situations are a risk to both eagles
and humans. The qualifications for
specific and general permits for nest
disturbance and nest take are
comparable to the standards established
in 2016. Additionally, the conditions for
our general permits will be based on the
conditions the Service commonly
requires in its current specific nest take
and nest disturbance permits. While we
are aiming to make applying easier for
project proponents by simplifying the
administrative process, we are not
making permits easier to secure in the
sense of relaxing requirements to protect
eagles.
The standards we are establishing
around general permits for take and
disturbance of bald eagle nests will
assure continued preservation of this
species for two reasons: First, because
those standards are based on the
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knowledge and experience we have
gained from issuing and monitoring
hundreds of permits over nearly two
decades, and second, a growing body of
scientific literature has demonstrated
that breeding bald eagles show a higher
tolerance and resilience to disturbance
and other impacts than previously
thought. We do not have comparable
data or experience in managing golden
eagle nests and have therefore not
opened the general-permit program up
to removal or disturbance of goldeneagle nests in this rulemaking.
We acknowledge and appreciate
Tribal concerns regarding the degree of
oversight required for general permits
when compared to specific permits. As
part of this final rule, we have added a
new eligibility restriction for nestdisturbance and nest-take activities in
Indian country, as defined in 18 U.S.C.
1151, after recent consultation with
Tribes. General permits will not be
available for nest take or nest
disturbance for nest structures located
in Indian country, unless requested by
the Tribe itself. Furthermore, the
Service will make publicly available a
list of all general permits issued, which
Tribes can review. We will be
implementing an audit program to
ensure that those participating in our
general permits are truly eligible and are
complying with the permits’ terms. For
specific permits, the Service will
continue to notify Tribes regarding
activities conducted on their lands.
Issue. Many Tribes believe the new
regulations remove opportunities for
Tribal engagement and bypass
government-to-government
consultation, especially for potential
impacts to Tribal lands or resources.
Response. Throughout all phases of
the rulemaking process, the Service has
encouraged and continues to welcome
government-to-government
consultation. In addition, we conducted
multiple information sessions
specifically for Tribes. The Service
acknowledges our Federal Tribal trust
responsibilities and deeply honors our
sovereign nation-to-nation relationship
with Tribes. To date, one Tribe
requested government-to-government
consultation regarding this regulation.
The Service made modifications to the
final rule based on this consultation. We
invite bilateral government-togovernment consultation at any time.
Wind Energy
Issue. Some commenters expressed
concerns about the cumulative impacts
of wind energy projects on the
landscape on eagle populations,
particularly at the LAP scale.
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Response. The Service has considered
at length how to implement general
permits for wind projects that are
consistent with the regulatory
preservation standard at the LAP scale.
The Service will use all available
information and the best available tools
to estimate where authorized take rates
may be the highest relative to our
estimated eagle-population densities.
Further, we will require Serviceapproved in-lieu fee programs to
allocate a small amount of
compensatory mitigation from each
general permittee to be available to
address LAP concerns. With these extra
mitigation funds, in-lieu fee programs
can deploy compensatory mitigation for
eagles in areas where LAP thresholds
are close to being exceeded (or have
been exceeded). If, after expenditure of
these funds, the Service still determines
that general-permit issuance is not
consistent with the preservation
standard, we retain the right to amend,
suspend, or revoke general permits in
order to safeguard local eagle
populations.
Issue. We received comments
regarding the take thresholds associated
with wind energy general permits,
including comments that such
thresholds are not necessary for bald
eagles, that such thresholds may cause
the general permit program to fail, and
requests to remove species-specific take
thresholds.
Response. The Service calculated the
take threshold for bald eagles and the
take threshold for golden eagles to
ensure general permitting is consistent
with the preservation of both eagle
species. The calculated threshold for
each species ended up being four eagles.
Ensuring take is compatible with eagle
preservation primarily depends on the
take rates for each eagle species, not the
combined take rate of eagles in general.
Therefore, there are separate take
thresholds for each species, not a
combined threshold for ‘‘eagles.’’
Finding four golden eagles creates a
fatality estimate similar to what we
would expect to see at an average-sized
project in the specific-permit zone.
Finding four bald eagles would produce
a similar result. However, a project that
discovers two dead bald eagles and two
dead golden eagles during one permit
term would be taking eagles at lower
rates than expected under specific
permits and, thus, a general permit is
appropriate.
In response to comments that general
permit take thresholds are not necessary
for bald eagles, we reiterate that the goal
of these thresholds is to ensure that the
Service has appropriately accounted for
the level of eagle take for projects
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receiving general permits in a way that
is consistent with our preservation
standard and ensure that projects with
relatively high risk to eagles (of either
species) are paired with the most
appropriate management actions that
are commensurate with higher or
uncertain take rates. Exceeding the
discovered eagles thresholds established
by these regulations is not a violation of
the permit. Rather, a project that
discovers more than established
thresholds indicates that there are
potentially unique circumstances at the
project site that would benefit from
Service engagement through the specific
permit process. The specific permit
process allows for Service review of
site-specific data and collaboration with
the permit applicant on development of
additional data collection and
avoidance and minimization approaches
appropriate for the project to ensure
permit issuance criteria are met and that
authorized take is consistent with our
preservation standard, particularly at
the local scale. This is not possible
under an automated general permit
process.
In response to the comment that the
general permit program is likely to fail,
our analysis of take in the general
permit zones suggests that it should be
a rare wind project in the general permit
zone that takes eagles at rates high
enough to discover four or more bald
eagles within a 5-year period. Our
estimates for even large wind projects in
the general permit zone are substantially
lower than estimated bald eagle
fatalities at a similar-sized project in the
specific permit zone, on which the foureagle threshold was based. Thus, we
expect that only a small proportion of
projects receiving general permits will
exceed the bald eagle threshold.
Issue. The Service received multiple
comments regarding the use of Evidence
of Absence software (Dalthrop et al.
2017) for specific permits; many of the
comments requested that the Service
eliminate the use of Evidence of
Absence software as a compliance
measure. Instead of Evidence of
Absence software, one commenter
suggested the Service should instead
assess compliance based on the actual
number of eagles found during fatality
monitoring.
Response. The Service recognizes the
limitations of Evidence of Absence
software. Therefore, on specific permits
the Service will authorize incidental
take of bald eagles, golden eagles, or
both but will not specify a take limit.
The Service will continue to use the
best available statistical programs to
evaluate and estimate mortality rates.
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Currently Evidence of Absence software
is the best estimator available to handle
zero-inflated data (i.e., data that has an
excess of zero counts). The Service will
use estimated mortality rates to
calculate compensatory mitigation
requirements. The Service will also use
estimated mortality rates to estimate the
number of eagles authorized for internal
tracking purposes. The Service will use
estimated mortality rates for eagles
instead of number of eagles found, as
this approach is more appropriate for
understanding how permit issuance
effects eagle populations.
Issue. Multiple comments expressed
disapproval of the Collision Risk Model
(CRM), with some stating the lack of
predictability with the CRM results in
increased costs and timelines.
Response. The Service recognizes
that, as with all models, we must
continue working to improve the CRM.
However, the CRM represents the best
science available today. The CRM was
developed using site-specific and
species-specific eagle exposure and
eagle collision data provided from wind
energy facilities across the Nation and
represents the best available data to
assess risk to eagles by turbines. The
Service’s CRM evaluates risk across
projects in a consistent and predictable
way while accounting and managing for
uncertainty. The Service uses sitespecific data to inform the CRM and
have the estimate reflect risk for a given
project while accounting for variability
in both eagle use and collision risk. In
the 2016 eagle rule and PEIS, the
Service described the adaptive
management framework for
authorization of eagle take. At wind
facilities, the Services uses monitoring
data—consistent with methods outlined
in the Land-Based Wind Energy
Guidelines (www.fws.gov/media/landbased-wind-energy-guidelines)—to
inform the initial take authorization for
a permit. We use monitoring data
collected under the permit to update the
estimates over time. Any mitigation
paid by the permittee initially that
exceeds updated take estimates is
credited forward, reducing future
mitigation burden.
The Service can evaluate alternative
models as part of the adaptive
management framework over time;
however, to ensure consistency and
adherence to management objectives,
initial permit estimates are based on our
peer-reviewed modeling framework.
Monitoring can be designed, in
coordination with the Service, to
compare updates to the CRM modeling
framework to results from other models.
Any comparison would need to evaluate
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9941
the model’s ability to quantify
uncertainty. Similarly, the Service’s
eagle permit biologists consider all sitespecific data available when thinking
about potential avoidance and
minimization measures that may reduce
risk at a given project, but rely on the
CRM and consistent, representative
monitoring data to represent risk across
all permitted projects. Site-specific data
(e.g., mortality monitoring) without use
of a model designed to extrapolate
beyond the monitoring period does not
appropriately account for variability in
eagle risk.
The Service will use the CRM to
calculate eagle fatalities for internal
tracking and calculating mitigation
requirements for specific permits. While
the Service generally does not
recommend that project proponents
propose an alternative CRM, under the
new rule Tier 2 specific permittees with
a reimbursable agreement may request
consideration of an alternative CRM.
The Service will review these requests
on a case-by-case basis and anticipates
requiring, at a minimum, publication of
the alternative CRM in the Federal
Register for public review at the cost of
the applicant, including quantification
of the uncertainty of the model (i.e.,
confidence in the estimate). The Service
may also require third-party monitoring
to validate the model.
Issue. Commenters requested
clarification on take limits associated
with the permits.
Response. Wind energy general
permits and specific permits will not
have a take limit associated with them.
Wind projects with a general permit
cannot discover four or more bald eagles
or four or more golden eagles within a
5-year permit term and remain eligible
for another general permit in the future.
We will continue to estimate take at
wind projects for both general and
specific permits to ensure consistency
with the preservation standard and, for
specific permits, determine required
compensatory mitigation. For specific
permits, the Service will require
additional compensatory mitigation if it
concludes (through data received in
annual reporting or otherwise) that
permitted take exceeds the level of
compensatory mitigation already
provided. If we determine that take at a
permitted facility is not consistent with
our preservation standard, we will
conduct an administrative check-in and
likely require amendments to the
permit.
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Required Determinations
Regulatory Planning and Review
(Executive Orders 12866, 13563, and
14094)
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Executive Order 12866 (E.O. 12866),
as reaffirmed by E.O. 13563 and E.O.
14094, provides that the Office of
Information and Regulatory Affairs
(OIRA) in the Office of Management and
Budget (OMB) will review all significant
rules. OIRA has determined that this
rulemaking action is significant.
Executive Order 14094 reaffirms the
principles of E.O. 12866 and E.O 13563
and states that regulatory analysis
should facilitate agency efforts to
develop regulations that serve the
public interest, advance statutory
objectives, and are consistent with E.O.
12866, E.O. 13563, and the Presidential
Memorandum of January 20, 2021
(Modernizing Regulatory Review).
Regulatory analysis, as practicable and
appropriate, shall recognize distributive
impacts and equity, to the extent
permitted by law. E.O. 13563
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emphasizes further that regulations
must be based on the best available
science and that the rulemaking process
must allow for public participation and
an open exchange of ideas. We have
developed this rule in a manner
consistent with these requirements.
Costs and benefits of the rule can be
broken down into three categories;
impacts to permittees, impacts to the
Service, and societal impacts. Impacts to
permittees include permitting costs as
described in Table 1, below, as well as
other unquantifiable costs such as the
costs associated with reading and
understanding the rule, time spent on
permit application, and costs associated
with training staff on the requirements
of the rule. Benefits to permittees
include the ability to acquire a permit
and eliminate the risk of enforcement
associated with incidental eagle take.
Where the costs of the proposed permit
exceed the benefits associated with the
risk of enforcement (e.g., projects with
low risk of incidental eagle take or
projects with perceived low risk of legal
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enforcement), we do not expect entities
to apply for a permit. Impacts to the
Service include costs associated with
processing and auditing these permits;
these costs are anticipated to be less
than the benefits of anticipated
reductions in staff time associated with
processing these permits, as general
permits can be issued without the need
for Service interaction. Societal impacts
include benefits associated with an
anticipated increase in eagle
populations associated with reduced
incidental take and beneficial activities
associated with compensatory
mitigation requirements; no societal
costs are assumed.
Table 1 below shows the permit count
and cost under the 2016 regulations, the
expected number of permits and average
permit costs under this rule, and the
estimated marginal costs and impacts
between the 2016 regulations and this
rule. Additional analysis is available in
the supporting FEA.
BILLING CODE 4333–15–P
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Table 1-Average Annual Cost and Permit Count Comparison Between 2016
Regulations and This Rule
2016 Regulations
Factors
Number
of
Annual
Permits
Fees and Costs per
Permit
Number
of Annual
Permits
Permit
Application
Fee
Administration
Fee
Wind Energy
Project (General)
Average
Compensatory
Mitigation
Costs
Average
Monitoring
Costs
Note: the current framework does
not include wind energy general
permits. The corresponding
existing type of permits are wind
energy specific permits, the
numbers and costs of which are
included below.
22 (Tier l);
52 (Tier 2)
Average Cost
Per Permit
Average
Annual Cost
to Industry
Permit
Application
Fee
Wind Energy
Project (Specific)
Administration
Fee
Average
Compensatory
Mitigation
Costs
Average
Monitoring
Costs
Average Cost
Per Permit
Average
Annual Cost
to Industrv
Administration
Fee
$1,000
$1,000
$2,500 (Tier 1)
$10,000 (Tier 2)
$2,500 (Tier 1)
$10,000 (Tier 2)
$37,200
$37,200
$0
$0
$40,700 (Tier 1)
$48,200 (Tier 2)
$40,700 (Tier 1)
$48,200 (Tier 2)
$3,401,800
$3,401,800
$18,000 (SP Tier 1)
$26,000 (SP Tier 2)
$82,000 (SP Tier 2 with
reimbursable agreement)
$36,000
$8,000
$10,000
$2,000
$960,000
$1,080,000
$120,000
$1,100,000
$1,100,000
$0
$2,104,000
$2,216,000
$112,000
$12,624,000
$13,296,000
$672,000
$1,000
$1,000
$2,500 (Tier 1)
$10,000 (Tier 2)
$2,500 (Tier 1)
$10,000 (Tier 2)
6
6
Note: the current framework does
not include power line entity
general permits
4 (Tier
1)0.2 (Tier
2)
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Average
Power Pole
Retrofit Costs
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($10,000)
(assumes that the average
project will be a SP Tier 2
oroiect)
Permit
Application
Fee
Power Line Entities
(General)
Fees and Costs per Permit
Marginal Cost Change from
2016 Regulations to this Rule
(savings in parentheses)
$0
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12FER2
$0
ER12FE24.010
Type of Permit
This Rule
9944
Average Cost
Per Permit
Nest Disturbance
(General)
Nest Disturbance
(Specific))
Nest Take (General)
Nest Take (Specific)
Average
Annnal Cost
to Industrv
Permit
Application
Fee
Compensatory
Mitigation
Costs
Monitoring
Costs
Average Cost
Per Permit
Average
Annual Cost
to Industry
Permit
Application
Fee
Compensatory
Mitigation
Costs
Monitoring
Costs
Average Cost
Per Permit
Average
Annual Cost
to Industry
Permit
Application
Fee
Compensatory
Mitigation
Costs
Monitoring
Costs
Average Cost
Per Permit
Average
Annual Cost
to Industry
Permit
Application
Fee
Compensatory
Mitigation
Costs
Monitoring
Costs
Average Cost
Per Permit
Average
Annual Cost
to Industry
96
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$16,200
$500
$500
$0
$0
$0
$0
$500
$500
$40,500
$40,500
$2,500
$2,500
$0
$0
$0
$0
$0
$0
$2,500
$2,500
$0
$240,000
$35,000
($205,000)
$500
$500
$0
$0
$0
$0
$500
$500
$17,000
$17,000
$2,500
$2,500
$0
$0
$0
$0
$0
$0
$2,500
$2,500
$0
$100,000
$15,000
($85,000)
$16,821,500
$3,857,500
$0
40
$0
142
The maximum total estimated annual
cost to industry for this rule is
$16,821,500. The maximum total
estimated cost over 5 years for all
permits is $84,107,500. The average
annual equivalent cost is $13,794,294
with a total net present value cost of
$68,971,471 using a 7 percent discount
rate. The average annual equivalent cost
is $15,407,509 with a total net present
value of $77,037,544 at a 3 percent
discount rate. These discount rates
represent a range of values that the
Office of Management and Budget
recommends as a Federal-program
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$16,200
Note: the current framework does
not include nest take general
permits. The corresponding
existing type of permits are nest
take specific permits, the numbers
and costs of which are included
below
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21:12 Feb 09, 2024
$3,500 (Tier I)
$11, 000 (Tier 2)
Note: the current framework does
not include nest disturbance
general permits. The corresponding
existing type of permits are nest
disturbance specific permits, the
numbers and costs of which are
included below
Average Annual Permits Counts and
Costs'
VerDate Sep<11>2014
$3,500 (Tier I)
$ 11, 000 (Tier 2)
$12,964,000
81
14
34
6
219
discount rate for benefit-cost analysis
for most Federal programs. The above
costs represent the total gross cost of the
rule and do not reflect the costs
associated with the existing regulations.
This rule is expected to create an
estimated maximum of $3,857,500 in
new costs annually and $19,287,500 in
new marginal costs over 5 years, as
compared to the 2016 regulations. These
estimates represent the maximum
quantifiable costs; they do not represent
other costs that may be incurred, such
as the costs for entities to read and
understand the rule, time spent on
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permit application, and costs associated
with training staff on the requirements
of the rule. However, these new
marginal costs are more than offset by
savings to both industry and the Service
in terms of reduced Eagle Act
enforcement costs and no requirements
for preconstruction monitoring under
general permits and the removed
requirement for third-party monitoring
under specific permits. The anticipated
74 wind-energy projects and 4 powerline entities that annually receive and
comply with a permit will no longer be
subject to potential enforcement under
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Federal Register / Vol. 89, No. 29 / Monday, February 12, 2024 / Rules and Regulations
the Eagle Act, which can result in
substantial legal costs, nor will they
incur costs to estimate and reduce their
legal risks, which may include
biological surveys and hiring staff and
attorneys. While this total reduced
enforcement cost is not quantifiable due
to limited data, the Service expects that
the savings exceed the total new costs
associated with this rule. The costs of
this rule are also offset by the
ecosystem-services benefits associated
with potential decreased take leading to
increased populations of eagles.
Regulatory Flexibility Act (5 U.S.C. 601
et seq.)
Under the Regulatory Flexibility Act
(5 U.S.C. 601 et seq., as amended by the
Small Business Regulatory Enforcement
Fairness Act (SBREFA) of 1996 (Pub. L.
104–121, 201, 110 Stat. 847)), whenever
an agency is required to publish a notice
of rulemaking for any proposed or final
rule, it must prepare and make available
for public comment a regulatory
flexibility analysis that describes the
effect of the rule on small businesses,
small organizations, and small
government jurisdictions. However, no
regulatory flexibility analysis is required
if the head of an agency certifies the rule
would not have a significant economic
impact on a substantial number of small
entities.
SBREFA amended the Regulatory
Flexibility Act to require Federal
agencies to provide the statement of the
factual basis for certifying that a rule
would not have a significant economic
impact on a substantial number of small
entities. Thus, for a regulatory flexibility
analysis to be required, impacts must
exceed a threshold for ‘‘significant
impact’’ and a threshold for a
‘‘substantial number of small entities.’’
See 5 U.S.C. 605(b). We examined this
rule’s potential effects on small entities
as required by the Regulatory Flexibility
Act and certify that this action will not
have a significant economic impact on
a substantial number of small entities.
This analysis first estimates the number
of businesses potentially impacted and
then estimates the economic impact of
this rule.
To assess the effects of this rule on
small entities, we focus on the proposed
general and specific permit approach for
incidental take by wind-energy facilities
and electric-transmission companies.
We also address nest disturbance and
nest take permits for businesses in other
sectors, such as housing and building
construction, railroads, timber
companies, pipeline companies, and
gold ore mining.
Using the North American Industry
Classification System (NAICS), the U.S.
Small Business Administration (SBA)
defines a small business as one with
9945
annual revenue or employment that
meets or is below an established size
standard. While the NAICS was updated
in 2023, we are using the 2017 NAICS
to best compare to the most recent 2017
Statistics of U.S. Businesses (SUSB)
tables that contain information on
receipts. Relevant 2017 NAICS small
business definitions include:
b fewer than 250 employees for
‘‘Wind Electric Power Generation’’
(NAICS sector 221115),
b fewer than 1,000 employees for
‘‘Electric Power Distribution’’ (NAICS
sector 221122),
b fewer than 500 employees for
‘‘Logging’’ (NAICS sector 113310),
b less than $36.5 million of average
annual receipts for ‘‘Construction of
Buildings’’ (NAICS sectors 236115,
236116, 236117, 236210, and 236220),
b less than $36.5 million of average
annual receipts for ‘‘Highway, Street,
and Bridge Construction’’ (NAICS sector
237310),
b less than $15.0 million of average
annual receipts for ‘‘Support Activities
for Rail Transportation’’ (NAICS sector
488210), and
b fewer than 1,500 employees for
‘‘Gold Ore Mining’’ (NAICS sector
212221).
Table 2 indicates the number of
businesses within each industry and the
estimated percentage of small
businesses impacted by this rule.
TABLE 2—DISTRIBUTION AND POTENTIAL IMPACT TO BUSINESSES 1
Total
firms/establishments
NAICS code
221115
221122
113310
236115
.....................
.....................
.....................
.....................
236116 .....................
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236117
236118
236210
236220
237310
237990
488210
212221
.....................
.....................
.....................
.....................
.....................
.....................
.....................
.....................
Description
Number of
all
businesses
Wind Electric Power Generation 2 .............................................
Electric Power Distribution 3 ......................................................
Logging 4 ...................................................................................
New Single-family Housing Construction (Except For-Sale
Builders) 4.
New Multifamily Housing Construction (Except For-Sale Builders) 4.
New Housing For-Sale Builders 4 .............................................
Residential Remodelers 4 ..........................................................
Industrial Building Construction 4 ..............................................
Commercial and Institutional Building Construction 4 ...............
Highway, Street, and Bridge Construction 4 .............................
Other Heavy and Civil Engineering Construction 4 ...................
Support Activities for Rail Transportation 4 ...............................
Gold Ore Mining 4 ......................................................................
Number of
small
businesses
Small businesses
potentially impacted
by this rule
Number
Percentage
459
1,233
7,992
49,215
135
1,169
7,977
49,143
22
0
up to 13
up to 13
16
0
<1
<1
3,175
2,851
up to 13
<1
15,483
103,079
2,997
38,079
8,826
4,165
564
147
15,099
102,998
2,847
36,100
8,198
4,052
484
132
up to 13
up to 13
up to 13
up to 13
up to 13
up to 13
up to 13
up to 2
<1
<1
1
<1
<1
<1
3
2
1 Data
is from the latest Statistics of U.S. Businesses (SUSB) tables that contain information on receipts, which is from 2017.
number of potentially impacted small businesses is based on the distribution of businesses by enterprise size from 2017 SUSB data tables, the total number of estimated annual permits, and the small business standards threshold from SBA.
3 Permitting will be required at a large utility scale similar to existing Special Purpose Utility permits (SPUT permits) that the Service issues.
4 We estimate that the number of nest disturbance and nest take permits will be similar to the number issued over the last 5 years: 677. The
non-electric and wind power generation NAICS represent sectors that have historically requested permits. We evenly distributed the estimated
total amount of disturbance and take permits across all sectors, with the exception of gold ore mining, for the 5-year period, which comes to 67
permits. Gold ore mining entities have historically applied for only 1 to 2 permits per year, or up to 10 over a 5-year period. We also assumed an
evenly distributed number of permits across each year, 13, for the remainder of the sectors.
2 The
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Federal Register / Vol. 89, No. 29 / Monday, February 12, 2024 / Rules and Regulations
In the last 5 years (2017 through
2022), the Service has issued 26 permits
to wind-energy generation facilities and
677 specific permits to other entities,
which averages about 141 permits
annually. For the 677 non-wind specific
permits, most were issued to businesses
and to government agencies, and the
remaining were issued to individuals.
The number of specific permits issued
under this rule over the first 5 years may
be higher or lower than the existing
permit program under the 2016
regulations due to the creation of
general permits and the remaining
complexity associated with specific
permits. General permits typically allow
the regulated community to apply for
and obtain a permit more easily,
particularly when projects are designed
at the outset to comply with generalpermit eligibility criteria. Specific
permits are available to wind-energyproject applicants that do not meet
general-permit eligibility criteria. Based
on these assumptions, we estimate that
the number of specific permits under
this rule will be similar to the number
of existing permits over the last 5 years,
which is close to 30 permits. Although
small, noncommercial, wind-energy
facilities (e.g., single-turbine facilities
connected to public buildings) could
apply for incidental take permits, we
anticipate that most of the applications
for wind-energy facilities will be for
utility-scale projects. The largest
expected impacts to small businesses
under this rule would be an increase in
the number of permits issued to windenergy generation facilities due to the
changes being made in the application
requirements and the availability of
general permits and the inclusion of
general and specific permits tailored to
power-line entities. We expect that this
rule will impact 16 percent of wind-
energy generation small businesses,
with the expected costs of such permits
described in tables 3 (general permits)
and 4 (specific permits), and a
breakdown of general permits by
enterprise size category in table 5.
Electric power distribution entities
are eligible for both general and specific
incidental take permits in the proposed
regulation. However, based on the
NAICS definitions, we assume that none
of the potential electric power
distribution permittees would be small
businesses.
Businesses that apply for nest take
and nest-disturbance permits typically
include home construction, road
construction, and various other
construction projects. We assume that
the number of nest take and nest
disturbance permits will continue along
this trend over the next 5 years. For this
analysis, we evenly distributed those
permits across industry sectors that best
represent the NAICS industry sectors
that applied for permits historically. We
anticipate the number of permit
applicants in those sectors would be
relatively small, on the order of 1 to 13
per year for each sector, except gold ore
mining, which historically applied for
only 1 to 2 permits annually. As a
result, this rule will impact less than 1
to 2.5 percent of small businesses in
NAICS sectors 236115, 236116, 236117,
236118, 236210, 236220, 237310,
237990, 488210, and 212221. The cost
per entity for nest take and nest
disturbance permitting under this rule is
minimal, totaling $100 per eagle or nest,
per year. The minimal cost of these
permits is not expected to result in a
significant impact to small businesses in
these sectors, regardless of the total
percentage of small businesses impacted
as a whole.
As described above, the wind-energy
generation industry is the only industry
for which specific and general permits
could result in a significant impact on
small businesses. Table 3 shows the
expected difference between 5-year
costs for specific permits and 5-year
costs for general permits for windenergy generation facilities. Windenergy generation facilities will pay less
for a general permit compared to the
costs associated with a standard permit
under the 2016 regulations. The permit
application fee (including costs for
auditing) is reduced from $36,000 to
$1,000 for a general permit. In addition,
applicants will pay an administration
fee of either $2,500 (Tier 1) or $10,000
(Tier 2), as compared to the existing
specific permit administration fee of
$8,000. Compensatory mitigation costs
for general permits for a wind-energy
project will average $37,200. This is a
significant decrease from the specificpermit cost under the 2016 regulations
of $960,000 (using our calculation from
the EA of $120,000 as the cost of an
eagle credit). The average costs for
monitoring for a wind-energy project
will be negligible, a cost savings from
the specific permit monitoring cost
estimates of $1,100,000 under the 2016
regulations. The total estimated cost
savings between a specific permit under
the 2016 regulations and a general
permit under this regulation is therefore
slightly over $2,000,000 per permit
(depending on whether the project is a
Tier 1 or a Tier 2 project). The total
number of estimated permits shows an
estimated overall increase in industry
costs associated with permitting under
this rule, but only because the Service
expects a substantial jump in
participation across industry due to the
improvements in the permit process and
reduction in costs and time required per
permit.
TABLE 3—WIND GENERAL PERMIT COSTS AND SAVINGS
[5-Year costs]
Specific—2016
regulations
(average)
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Cost category
General—this rule
(average)
Cost savings
(average)
Permit application fee .............................
Administration Fee .................................
Compensatory Mitigation Costs .............
Monitoring Costs ....................................
$36,000
8,000
960,000
1,100,000
$1,000 ....................................................
2,500 (Tier 1); 10,000 (Tier 2) ...............
37,200 ....................................................
0 .............................................................
$35,000.
5,500 (Tier 1); (2,000) (Tier 2).
922,800.
1,100,000.
Total Cost ........................................
2,104,000
40,700 (Tier 1); 48,200 (Tier 2) .............
2,063,300 (Tier 1); 2,055,800 (Tier 2).
Table 4 displays the new cost for
specific permits under this rule
compared to the cost for specific
permits under the 2016 regulations.
Under this rule, entities will pay
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$1,080,000 for compensatory mitigation,
an increase of $120,000 from the
$960,000 cost under the 2016
regulations. These costs have increased
due to updates in the estimated amount
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Fmt 4701
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of required mitigation for projects in the
specific-permit category. The Service
may issue three types of wind-energy
specific permits under this rule. Tier 1
permits are for the simplest types of
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Federal Register / Vol. 89, No. 29 / Monday, February 12, 2024 / Rules and Regulations
projects and would require a $10,000
permit-application cost. Tier 2 permits
are similar to existing specific permits
and require a $26,000 permit
application cost. Tier 2 with
reimbursable agreement permits require
permittees to pay for staff time via a
9947
regulations. Entities will continue to
pay their own monitoring costs
estimated at $1,100,000 over the life of
the permit. As a result, the total average
cost increase to entities receiving a
wind-energy specific permit under this
rule is $112,000.
reimbursable agreement above and
beyond the $26,000 permit application
cost. For purposes of this analysis, we
assume that the average specific permit
will be a Tier 2 permit with the same
permit-application cost as the specificpermit structure under the 2016
TABLE 4—WIND ENERGY SPECIFIC PERMIT COSTS AND SAVINGS
[5-Year costs]
Specific—2016
regulations
(average)
Cost category
Specific—
this rule
(average)
Cost savings
(average)
Permit Application Fee ............................................................................................................
Administration Fee ...................................................................................................................
Compensatory Mitigation Costs ...............................................................................................
Monitoring Costs ......................................................................................................................
$36,000
8,000
960,000
1,100,000
$26,000
10,000
1,080,000
1,100,000
$10,000
(2,000)
(120,000)
0
Total Cost .........................................................................................................................
2,104,000
2,216,000
(112,000)
projected percentage of receipts
impacted by this rule both at the
individual establishments level and the
total for that enterprise size. The windenergy project general-permit cost will
be paid in full at the time of the permit
application; therefore, the 5-year cost of
$48,200 is assessed in the first year.
This cost would then be assessed again
at the renewal of the permit in 5 years.
Due to this being a one-time cost that
covers a 5-year period, this amount
equates to at most one percent of total
annual receipts by enterprise size (table
Businesses in the ‘‘wind electric
power generation industry’’ are defined
as small if they have fewer than 250
employees. The 2017 SUSB Annual
Data Tables report the annual payroll
amounts by industry that fall within
enterprise size categories. The data for
‘‘wind electric power generation’’ does
not contain a range for businesses with
under 250 employees; the closest
reporting range is fewer than 500
employees. Table 5 shows a range of
receipts by enterprise size and
establishment count as well as the
5). As a result, this cost will not create
a substantial impact on small businesses
or specific industries. We base this
determination on permit costs for
general permits. The number of specific
permits issued is expected to follow the
same trend as under the 2016
regulations, and permits are likely to be
issued in areas of higher risk to eagles
to large, complex facilities that are well
above the industry-standard payroll
amount. Therefore, we do not expect
any impacts to small businesses
associated with these specific permits.
TABLE 5—RANGE OF RECEIPTS IMPACTED BY THIS RULE: WIND ELECTRIC POWER GENERATION GENERAL PERMITS
[Using 2017 SUSB annual data table]
Enterprise size 1
01:
02:
03:
04:
05:
06:
12:
19:
24:
25:
26:
Annual
receipts
($1,000)
Establishments
Total ..........................................
<5 employees ...........................
5–9 employees ..........................
10–14 employees ......................
15–19 employees ......................
<20 employees .........................
50–74 employees ......................
<500 employees .......................
2,000–2,499 employees ............
2,500–4,999 employees ............
5,000+ employees ....................
459
45
8
7
8
68
9
135
12
11
240
$8,001,761
80,905
14,478
15,873
39,960
151,216
98,897
1,469,292
75,879
91,973
5,368,670
Average
receipt
for size
(=receipt/
establishments)
($1,000)
Annual cost
per permit for
establishment
$17,433
1,798
1,810
2,268
4,995
2,224
10,989
10,884
6,323
8,361
22,369
Number of
establishments
impacted
annually 2
$48,200
48,200
48,200
48,200
48,200
48,200
48,200
48,200
48,200
48,200
48,200
74
7
1
1
1
11
1
22
2
2
39
Total
annual %
of receipts
impacted by
this rule
0.04
0.42
0.33
0.30
0.12
0.35
0.05
0.07
0.13
0.10
0.04
Annual %
of receipts for
impacted
establishments
0.3
2.7
2.7
2.1
1.0
2.2
0.4
0.4
0.8
0.6
0.2
1 2017
NAICS thresholds for ‘‘Wind Electric Power Generation’’ (NAICS 221115) define small businesses as having fewer than 250 employees.
number of establishments impacted annually is based on the weighting of the number of establishments in that enterprise size compared to the total number
of establishments. That weight value was multiplied by the total number of estimated annual permits (74) to derive the figures shown. Note that the total sum of <500
and the enterprise sizes greater than 500 will not total 74 due to missing enterprise size categories from the SUSB 2017 data tables.
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2 The
While electric-power-distribution
companies are currently eligible to
apply for a specific permit, under this
rule, these entities are eligible to apply
for general permits. The permit
application fee for these general permits
is $1,000, and the administration fee is
either $2,500 (for Tier 1 permittees) or
$10,000 (for Tier 2 permittees). The
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costs for power-pole retrofits called for
under the proactive retrofit strategy are
estimated to be $0. Many larger utilities
already have existing avian protection
and retrofit strategies in place and
would not incur new costs or benefits
associated with the proposed retrofit
strategy. For entities without an avian
protection plan and a retrofit strategy in
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place, we expect that the retrofit
requirement for a general permit will
not create substantial new costs for
those entities. Any costs associated with
retrofitting power poles to be avian-safe
(estimated from approximately $500–
$2,500 per pole) would be at least partly
recouped by increased reliability and a
reduction in costs associated with eagle-
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Federal Register / Vol. 89, No. 29 / Monday, February 12, 2024 / Rules and Regulations
electrocution response. The Service
assumes that the primary interest in
permits in the first 5 years would be
from firms with existing specialpurpose-utility permits to salvage dead
birds. These firms with known
incidental take of eagles will benefit
from a permit authorizing that take. No
existing special-purpose-utility permit
holder is a small business, and,
therefore, there will not be a substantial
impact to small businesses from this
rule.
A commercial business applying for a
standard nest disturbance or nest take
permit under the 2016 regulations
would have to pay $500 per nest per
year, while a noncommercial entity
would pay $100 per nest per year.
Under this rule, both commercial and
noncommercial permittees would pay
$100 per nest per year for a general
permit. Businesses in the construction
industry are defined as small if they
have annual revenue less than $36.5
million. Depending on the type of
permit applications submitted by an
individual small business, the permit
fees represent less than one percent of
revenue. Thus, the creation of a general
permit will not have a significant
economic effect on a substantial number
of small businesses in the construction
sectors. The changes in general permit
application fees are shown in tables 6
and 7. The costs of a specific permit for
both nest disturbance and nest take
would be unchanged from the existing
regulation.
Table 6 shows the expected difference
between the 5-year costs for a nestdisturbance permit under the 2016
regulations and a general permit under
this rule.
TABLE 6—NEST DISTURBANCE GENERAL PERMIT COSTS AND SAVINGS
[5-Year costs]
Cost category
Nest disturbance—
2016 regulations
Nest disturbance—
this rule
Cost savings
Permit application costs .......................................................................................
$2,500
$500
$2,000
Table 7 shows the expected difference
between the 5-year costs for a nest-take
permit under the 2016 regulations and
a general permit under this rule.
TABLE 7—NEST TAKE GENERAL PERMIT COSTS AND SAVINGS
khammond on DSKJM1Z7X2PROD with RULES2
[5-Year costs]
Cost category
Nest take—
2016 regulations
Nest take—
this rule
Cost savings
Permit Application Costs .....................................................................................
$2,500
$500
$2,000
This rule is expected to create an
overall savings due to reduced costs for
general permits compared to specific
permits under the 2016 regulations.
This rule is expected to create
additional savings to both industry and
the Service in terms of reduced Eagle
Act enforcement costs. Entities that
receive and comply with a permit will
no longer be subject to potential
enforcement under the Eagle Act, which
can result in substantial legal costs, nor
will they incur costs to estimate and
reduce their legal risks, which may
include biological surveys and hiring
staff and attorneys. While this total
reduced enforcement cost is not
quantifiable due to limited data, the
Service expects that it exceeds the total
of new costs associated with this rule.
In sum, this rule impacts a substantial
number of small businesses in NAICS
sector 221115, ‘‘Wind Electric Power
Generation’’; however, the economic
impacts to individual businesses are not
significant. As described above, the
number of businesses belonging to other
industries impacted is not substantial
and the magnitude of those economic
impacts is not significant. Based on the
available information analyzed above,
we certify that this rule will not have a
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significant economic effect on a
substantial number of small entities as
defined under the Regulatory Flexibility
Act (5 U.S.C. 601 et seq.). Therefore, a
regulatory flexibility analysis is not
required, and a small entity compliance
guide is not required.
Unfunded Mandates Reform Act (2
U.S.C. 1501 et seq.)
In accordance with the Unfunded
Mandates Reform Act, we have
determined the following:
a. This rule will not ‘‘significantly or
uniquely’’ affect small governments in a
negative way. There would be no permit
administration costs incurred by small
governments because they would not be
administering the issuance of Federal
permits. Small governments could
potentially apply for permits for nest
take or nest disturbance, but fees for
those permits are small and would not
significantly affect small governments in
a negative way. A small government
agency plan is not required.
b. This rule will not produce a
Federal mandate of $100 million or
greater in any year. It is not a
‘‘significant regulatory action’’ under
the Unfunded Mandates Reform Act.
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Takings (E.O. 12630)
In accordance with E.O. 12630, this
rule will not have significant takings
implications. This rule does not contain
any provisions that could constitute
taking of private property. Therefore, a
takings implication assessment is not
required.
Federalism (E.O. 13132)
This rule will not have sufficient
federalism effects to warrant preparation
of a federalism summary impact
statement under E.O. 13132. It will not
interfere with the States’ abilities to
manage themselves or their funds. No
significant economic impacts are
expected to result from the regulations
changes.
Civil Justice Reform (E.O. 12988)
In accordance with E.O. 12988, the
Office of the Solicitor has determined
that this rule does not unduly burden
the judicial system and meets the
requirements of sections 3(a) and 3(b)(2)
of the Order.
Paperwork Reduction Act (44 U.S.C.
3501 et seq.)
This rule contains existing and new
information collections. All information
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Federal Register / Vol. 89, No. 29 / Monday, February 12, 2024 / Rules and Regulations
collections require approval by the
Office of Management and Budget
(OMB) under the Paperwork Reduction
Act of 1995 (PRA, 44 U.S.C. 3501 et
seq.). We may not conduct or sponsor,
and you are not required to respond to,
a collection of information unless it
displays a currently valid OMB control
number. The OMB has reviewed and
approved the information collection
requirements associated with eagle
permits and fees and assigned the OMB
Control Number 1018–0167.
In accordance with the PRA and its
implementing regulations at 5 CFR
1320.8(d)(1), we provide the general
public and other Federal agencies with
an opportunity to comment on our
proposal to revise OMB Control Number
1018–0167. This input will help us
assess the impact of our information
collection requirements and minimize
the public’s reporting burden. It will
also help the public understand our
information collection requirements and
provide the requested data in the
desired format.
As part of our continuing effort to
reduce paperwork and respondent
burdens, and in accordance with 5 CFR
1320.8(d)(1), we invite the public and
other Federal agencies to comment on
any aspect of this proposed information
collection, including:
(1) Whether or not the collection of
information is necessary for the proper
performance of the functions of the
agency, including whether or not the
information will have practical utility;
(2) The accuracy of our estimate of the
burden for this collection of
information, including the validity of
the methodology and assumptions used;
(3) Ways to enhance the quality,
utility, and clarity of the information to
be collected; and
(4) Ways to minimize the burden of
the collection of information on those
who are to respond, including through
the use of appropriate automated,
electronic, mechanical, or other
technological collection techniques or
other forms of information technology,
e.g., permitting electronic submission of
response.
Comments that you submit in
response to this rulemaking are a matter
of public record. Before including your
address, phone number, email address,
or other personal identifying
information in your comment, you
should be aware that your entire
comment—including your personal
identifying information—may be made
publicly available at any time. While
you can ask us in your comment to
withhold your personal identifying
information from public review, we
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cannot guarantee that we will be able to
do so.
The Bald and Golden Eagle Protection
Act (Eagle Act; 16 U.S.C. 668–668d)
prohibits take of bald eagles and golden
eagles except pursuant to Federal
regulations. The Eagle Act regulations at
title 50, part 22 of the CFR define the
‘‘take’’ of an eagle to include the
following broad range of actions: To
‘‘pursue, shoot, shoot at, poison, wound,
kill, capture, trap, collect, destroy,
molest, or disturb.’’ The Eagle Act
allows the Secretary of the Interior to
authorize certain otherwise prohibited
activities through regulations. Service
permit applications associated with
eagles are each tailored to a specific
activity based on the requirements for
specific types of permits. We collect
standard identifier information for all
permits. The information that we collect
on applications and reports is the
minimum necessary for us to determine
if the applicant meets/continues to meet
issuance requirements for the particular
activity. Standardizing general
information common to the application
forms makes filing of applications easier
for the public as well as expedites our
review of applications. In accordance
with Federal regulations at 50 CFR
13.12, we collect standard identifier
information for all permits, including
the following:
• Applicant’s full name and address
(street address, city, county, State, and
zip code; and mailing address if
different from street address); home and
work telephone numbers; and a fax
number and email address (if available),
and
—If the applicant resides or is located
outside the United States, an address
in the United States, and, if
conducting commercial activities, the
name and address of his or her agent
that is located in the United States;
and
—If the applicant is an individual, the
date of birth, occupation, and any
business, agency, organizational, or
institutional affiliation associated
with the wildlife or plants to be
covered by the license or permit; or
—If the applicant is a business,
corporation, public agency, or
institution, the tax identification
number; description of the business
type, corporation, agency, or
institution; and the name and title of
the person responsible for the permit
(e.g., president, principal officer, or
director);
• Location where the requested
permitted activity is to occur;
• Reference to the part(s) and
section(s) of subchapter B as listed in 50
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9949
CFR 13.11(b) under which the
application is made for a permit or
permits, together with any additional
justification, including supporting
documentation as required by the
referenced part(s) and section(s);
• If the requested permitted activity
involves the import or reexport of
wildlife or plants from or to any foreign
country, and the country of origin, or
the country of export or re-export
restricts the taking, possession,
transportation, exportation, or sale of
wildlife or plants, documentation as
indicated in 50 CFR 14.52(c);
• Certification containing the
following language:
—I hereby certify that I have read and
am familiar with the regulations
contained in title 50, part 13, of the
Code of Federal Regulations and the
other applicable parts in subchapter B
of chapter I of title 50, Code of Federal
Regulations, and I further certify that
the information submitted in this
application for a permit is complete
and accurate to the best of my
knowledge and belief. I understand
that any false statement herein may
subject me to suspension or
revocation of this permit and to the
criminal penalties of 18 U.S.C. 1001.
• Desired effective date of permit
(except where issuance date is fixed by
the part under which the permit is
issued);
• Date;
• Signature of the applicant; and
• Other information that the Director
determines relevant to the processing of
the application, including, but not
limited to, information on the
environmental effects of the activity
consistent with 40 CFR 1506.5 and
Departmental procedures at 516 DM 8.
In addition to the general permitting
requirements outlined in Federal
regulations at 50 CFR 13.12,
applications for any permit under 50
CFR part 22 must contain:
• Species of eagle and number of
birds, nests, or eggs proposed to be
taken, possessed, or transported;
• Specific locality in which taking is
proposed, if any;
• Method of proposed take, if any;
• If not taken, the source of eagles
and other circumstances surrounding
the proposed acquisition or
transportation;
• Name and address of the public
museum, public scientific society, or
public zoological park for which they
are intended; and
• Complete explanation and
justification of the request, nature of
project or study, number of specimens
now at the institution, reason these are
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Federal Register / Vol. 89, No. 29 / Monday, February 12, 2024 / Rules and Regulations
inadequate, and other appropriate
explanations.
The proposed revisions to existing
and new reporting and/or recordkeeping
requirements identified below require
approval by OMB:
(1) Administrative Updates—On
January 7, 2022, the Service published
a final rule (87 FR 876) making
administrative updates to 50 CFR parts
21 and 22. We captured the associated
administrative updates to the CFR
references for part 22 in the updated
versions of the forms in this collection
being submitted to OMB for approval
with this renewal/revision request.
(2) Change in Administration Fees—
State, Local, Tribal, or Federal Agencies
(§ 13.11(d)(3)(i))—This rule changes the
Service’s practice of not charging
administration fees for eagle permits
under 50 CFR part 22 to any State, local,
Tribal, or Federal government agency, or
to any individual or institution acting
on behalf of the agency. Except as
otherwise authorized or waived, if the
agency fails to submit evidence of
agency status with the application, we
will require the submission of all
processing fees prior to the acceptance
of the application for processing.
(3) Revision to Form 3–200–71—We
split approved Form 3–200–71, ‘‘Eagle
Take Associated with but not the
Purpose of an Activity (Incidental
Take)’’ into two separate forms * as
follows:
a. Form 3–200–71, ‘‘Eagle Incidental
Take’’—General and Specific, and
b. Form 3–200–91, ‘‘Eagle Disturbance
Take’’—General and Specific.
khammond on DSKJM1Z7X2PROD with RULES2
* With this submission, we are no longer
proposing Form 3–200–92, Eagle Incidental
Take (Power Lines)—General and Specific.’’
We further describe the changes
below:
a. (Revised Title) Form 3–200–71,
‘‘Eagle Incidental Take’’—General and
Specific—The revision to Form 3–200–
71 authorizes the incidental take of
eagles where the take results from but is
not the purpose of an activity. General
permits are valid for 5 years from the
date of registration. Specific permits
may be valid for up to 30 years. In
addition to the standardized
information required by 50 CFR 13.12,
permit application requirements include
submission of the following
information:
i. Requested permit type;
ii. Infrastructure type;
iii. Description, duration, and location
of the activity that is likely to cause
eagle take;
iv. Justification of why there is no
practicable alternative to the activity
that would protect the interest to be
served;
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v. Description of eagle use and
activity in the area, location of eagle
nests or roosts, and distance of nests
and other important eagle use areas
from the project;
vi. Identification of subpermittees, if
applicable;
vii. Records retention requirements;
viii. Certification of activity’s
compliance with all Federal, Tribal,
State, and local laws and regulations
applicable to eagles; and
ix. Permit disqualification factors,
including information for any
convictions, guilty pleas or nolo
contendere, forfeited collateral, or
pending charges for violations of laws
cited in the permit application.
General permit applications must also
include the compensatory mitigation
requirement, requested permit tenure
and effective date, and certification of
general permit requirements. Additional
information collected from specific
permit applicants includes:
i. Requested duration of the permit;
ii. Requested eagle species for
authorization;
iii. Additional project-specific
information, including an eagle impacts
assessment and pre- or postconstruction monitoring methods;
iv. Description of implemented and
proposed avoidance and minimization
measures;
v. Description of implemented and
proposed compensatory mitigation;
vi. Existing project general permit
eligibility, if applicable; and
vii. Anticipated permit application fee
tier.
Permit applications associated with
eagle incidental take permits may
require the following:
• Post-Construction Monitoring—
Post-construction monitoring fatality
estimation must be based on 2 or more
years of eagle fatality monitoring that
meet the Service’s minimum fatality
monitoring requirements for specific
eagle permits.
• Adaptive Management Plan—Upon
the discovery of the third and fourth
bald eagle or golden eagle injuries or
mortalities at a project, the permittee
must provide the Service with their
reporting data required by the permit
conditions, adaptive management plan,
and a description and justification of
which adaptive management
approaches will be implemented.
• Annual Report—Permittees must
submit an annual report using Form 3–
202–15. The annual report is due within
30 days of the expiration of the permit
or prior to requesting renewal of the
permit, whichever is first.
• Compensatory Mitigation—For
wind energy specific permits, the
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permittee must implement the
compensatory mitigation requirements
on the face of their permit. For wind
energy general permits, the permittee
must obtain eagle credits from a Serviceapproved conservation bank or in-lieu
fee program based on the hazardous
volume of the project.
In addition, permit applications
associated with incidental take permits
by power lines may require the
following:
• Collision Response Strategy—A
plan that describes the process the
permittee will follow to identify
whether a collision-caused injury or
morality has occurred, to evaluate
factors that contributed to the collision,
and to implement risk-reduction
measures commensurate with the
collision risk.
• Proactive Retrofit Strategy—A plan
to convert existing infrastructure to
avian-safe infrastructure within a set
timeline. The strategy must identify a
baseline of poles to be proactively
retrofit. The existing-infrastructure
baseline must include all poles that are
not avian-safe for eagles located in areas
identified by the applicant to be high
risk to eagles and may also include
other poles in the service area.
• Reactive Retrofit Strategy—A plan
to respond to incidents where eagles are
electrocuted or killed. The reactive
retrofit strategy must include
information on how eagle electrocutions
are detected and identified. Determining
which poles to retrofit must be based on
the risk to eagles and not on other
factors (e.g., convenience or cost). The
pole that caused the electrocution must
be retrofitted unless the pole is already
avian-safe. A total of 13 poles or a halfmile segment must be retrofitted,
whichever is less, prioritizing the
highest risk poles closest to the
electrocution event.
• Shooting Response Strategy—A
plan that describes the process the
permittee will follow when eagles are
found killed or injured near power-line
infrastructure to identify if shooting is
suspected, to communicate with law
enforcement, and to identify and
implement appropriate shooting
reduction measures.
The Service will use the information
collected via the form to track whether
the take level is exceeded or is likely to
be exceeded, to determine that the take
is necessary, and that the take will be
compatible with the preservation of
eagles.
b. (NEW) Form 3–200–91, ‘‘Eagle
Disturbance Take’’—General and
Specific—Applicants may apply for an
eagle disturbance take permit if their
activity may result in incidental
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disturbance of bald eagles or golden
eagles. General permits issued under
this section are available only for certain
activities that cause disturbance of bald
eagles and are valid for a maximum of
1 year. General permits are not available
for disturbance of nests located in
Indian country (18 U.S.C. 1151), unless
the Tribe is the applicant. Specific
permits are intended for disturbance of
a golden eagle nest, disturbance of a
bald eagle nest by an activity not
specified in paragraph (b) of § 22.280, or
disturbance of eagles caused by physical
or functional elimination of all foraging
area within a territory. The tenure of
specific permits is set forth on the face
of the permit and may not exceed 5
years. In addition to the standardized
information required by 50 CFR 13.12,
permit application requirements include
submission of the following
information:
i. Requested permit type;
ii. Description, duration, and location
of the activity that is likely to cause
disturbance to eagles;
iii. Justification of why there is no
practicable alternative to the activity
that would protect the interest to be
served;
iv. Description of eagle use and
activity in the area, location of eagle
nests or roosts, and distance of nests
and other important eagle use areas
from the project;
v. Identification of subpermittees, if
applicable;
vi. Records retention requirements;
vii. Certification of activity’s
compliance with all Federal, Tribal,
State, and local laws and regulations
applicable to eagles; and
viii. Permit disqualification factors,
including information for any
convictions, guilty pleas or nolo
contendere, forfeited collateral, or
pending charges for violations of laws
cited in the permit application.
General permit applications must also
include the requested permit tenure and
effective date and certification of
general permit requirements. Additional
information collected from specific
permit applicants includes:
i. Organization status (e.g.,
commercial or non-commercial);
ii. Requested duration of the permit;
iii. Assessment of impacts to eagles;
iv. Description of implemented and
proposed avoidance and minimization
measures;
v. Description of implemented and
proposed compensatory mitigation for
golden eagle nest disturbance, if
applicable; and
vi. Description of efforts to monitor
for impacts to eagles.
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Permit applications associated with
eagle disturbance take may require the
following:
• Monitoring—The permittee must
monitor the nest to determine whether
nestlings have fledged from the nest. We
updated the burden for monitoring
requirements associated with
disturbance take in the separate
monitoring information collection
requirement.
• Annual Report—Permittees must
submit an annual report using Form 3–
202–15. The annual report is due within
30 days of the expiration of the permit
or prior to requesting renewal of the
permit, whichever is first.
The Service will use the information
collected via the form to track whether
the take level is exceeded or is likely to
be exceeded, to determine that the take
is necessary, and that the take will be
compatible with the preservation of
eagles.
(4) Revision to Form 3–200–72—We
are revising Form 3–200–72, ‘‘Eagle
Nest Take’’ as described below:
Form 3–200–72 is used to apply for
authorized take of bald eagle nests or
golden eagle nests, including relocation,
removal, and otherwise temporarily or
permanently preventing eagles from
using the nest structure for breeding
under definitions in 50 CFR 22.300(b).
General permits are available for bald
eagle nest take for emergency, nest take
for health and safety, or nest take for a
human-engineered structure, or, if
located in Alaska, other purposes.
General permits may authorize bald
eagle nest removal from the nesting
substrate at the location requested and
the location of any subsequent nesting
attempts by the eagle pair within onehalf mile of the location requested for
the duration of the permit. Take of an
additional eagle nest(s) more than onehalf mile away requires additional
permit(s). General permits are valid
until the start of the next breeding
season, not to exceed 1 year. General
permits are not available for take of
nests located in Indian country (18
U.S.C. 1151), unless the Tribe is the
applicant. Specific permits are required
for take of a golden eagle nest for any
purpose, take for species protection,
and, except for Alaska, nest take for
other purposes. The tenure of specific
permits is set forth on the face of the
permit and may not exceed 5 years.
In addition to the standardized
information required by 50 CFR 13.12,
permit application requirements include
submission of the following
information:
a. Requested permit type;
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b. Description and location of the
activity that will result in eagle nest
take;
c. Selected purpose of nest take;
d. Justification of why there is no
practicable alternative to the activity
that would protect the interest to be
served;
e. Description of the nest(s), including
species, location, and historic and
current nest status;
f. Description of nest removal,
destruction, or relocation, including
information related to re-nesting and
donation of eagle nests and parts.
g. Identification of subpermittees, if
applicable;
h. Records retention requirements;
i. Certification of activity’s
compliance with all Federal, Tribal,
State, and local laws and regulations
applicable to eagles; and
j. Permit disqualification factors,
including information for any
convictions, guilty pleas or nolo
contendere, forfeited collateral, or
pending charges for violations of laws
cited in the permit application.
General permit applications must also
include the requested permit tenure and
effective date and certification of
general permit requirements. Additional
information collected from specific
permit applicants includes:
i. Organization status (e.g.,
commercial or non-commercial);
ii. Requested duration of the permit;
iii. Assessment of impacts to eagles;
iv. Description of implemented and
proposed avoidance and minimization
measures;
v. Description of implemented and
proposed compensatory mitigation for
golden eagle nest take, if applicable;
vi. Description of efforts to monitor
for impacts to eagles; and
vii. Description of method for
removing nestlings or eggs and
proposed disposition, if applicable.
Permit applications associated with
eagle nest take may require the
following:
• Monitoring—Permittees must
remove chicks or eggs from an in-use
nest for immediate transport to a foster
nest, rehabilitation facility, or as
otherwise directed by the Service. If
nestlings or eggs are relocated with a
nest or to a foster nest, the permittee
must monitor the nest to ensure adults
are tending to nestlings or eggs. We
updated the burden for monitoring
requirements associated with eagle nest
take in the separate monitoring
information collection requirement.
• Annual Report—Permittees must
submit an annual report using Form 3–
202–16. The annual report is due within
30 days of the expiration of the permit
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or prior to requesting renewal of the
permit, whichever is first.
• Species Protection—If a Federal,
State, or Tribal agency applies for a nest
take permit for species protection, they
must provide documentation that
describes relevant management efforts
to protect the species of concern;
identifies and describes how the nesting
eagles are a limiting factor to recovery
of the species using the best available
scientific information and data; and
explains how take of eagle nests is likely
to have a positive effect on recovery for
the species of concern.
The Service will use the information
collected via the form to track whether
the take level is exceeded or is likely to
be exceeded, to determine whether the
take is necessary, and whether the take
will be compatible with the preservation
of eagles.
(5) Permit Reviews—The Service
removed the regulatory requirement for
specific permits to mandate an
administrative check-in with the Service
at least every 5 years during the permit
tenure. The Service introduced these
mandatory 5-year permit reviews as part
of the 2016 Eagle Rule to ensure that the
Service had an opportunity to ask for
and review all existing data related to a
long-term activity’s impacts on eagles.
The purpose of 5-year review is to
update take estimates and related
compensatory mitigation for the
subsequent 5-year period. It also
provides the Service with an
opportunity to amend the permit to
reduce or eliminate conservation
measures or other permit conditions
that prove to be ineffective or
unnecessary. The purpose of these
reviews does not change with this
rulemaking. However, the 5-year
requirement has introduced unintended
uncertainty which, according to public
comment, has reduced participation in
eagle take permitting under the 2016
regulations. It has also resulted in
timing issues, where post-construction
monitoring or other data is available offcycle from the 5-year timing (e.g., year
3 or 4) but cannot be used until the
scheduled check-in. Instead, check-ins
may now be initiated by the permittee
or the Service in response to events that
warrant review, for example, updating
fatality estimates and associated
compensatory mitigation requirements
or revising permit conditions to reflect
the best available science.
(6) Reporting Requirements—
Submission of reports is generally on an
annual basis, although some are
dependent on specific transactions.
Additional monitoring and report
requirements exist for permits issued
under 50 CFR part 22. Permittees must
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submit an annual report for every year
the permit is valid and for up to 3 years
after the activity is completed.
a. (New Reporting Requirement)
Report Take of Eagles (3rd and 4th
Eagles) (50 CFR 22.250(d)(2) and
(d)(3))—Permittees must notify the
Service in writing within 2 weeks of
discovering the take of a third or fourth
bald eagle or a third or fourth golden
eagle. The notification must include the
reporting data required in their permit
conditions, their adaptive management
plan, and a description and justification
of which adaptive management
approaches they will be implementing.
Upon notification of the take of the
fourth bald eagle or fourth golden eagle,
the project will remain authorized to
incidentally take eagles through the
term of the existing general permit but
will not be eligible for future general
permits.
(7) (NEW) Audits—The Service will
conduct audits of general permits to
ensure permittees are appropriately
interpreting and applying eligibility
criteria and complying with permit
conditions. Audits may include
reviewing application materials for
completeness and general permit
eligibility. Any required records, plans,
or other documents will be requested of
the permittee and reviewed. If there is
a compliance concern, the applicant
will be given the opportunity to submit
additional information to address the
concern. If, during an audit, the Service
determines that the permittee is not
eligible for a general permit or is out of
compliance with general permit
conditions, we will communicate to the
permittee options for coming into
compliance.
(8) (NEW—Existing In Use Without
OMB Approval) Labeling Requirement—
Regulations at 50 CFR 22.4 require all
shipments containing bald or golden
eagles, alive or dead, their parts, nests,
or eggs to be labeled. The shipments
must be labeled with the name and
address of the person the shipment is
going to, the name and address of the
person the shipment is coming from, an
accurate list of contents by species, and
the name of each species.
(9) (NEW—Existing In Use Without
OMB Approval) Requests for
Reconsideration Associated with Eagle
Permits (Suspension and Revocation)—
Persons notified of the Service’s
intention to suspend or revoke their
permit may request reconsideration by
complying with the following:
• Within 45 calendar days of the date
of notification, submit their request for
reconsideration to the issuing officer in
writing, signed by the person requesting
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reconsideration or by the legal
representative of that person.
• The request for reconsideration
must state the decision for which
reconsideration is being requested and
shall state the reason(s) for the
reconsideration, including presenting
any new information or facts pertinent
to the issue(s) raised by the request for
reconsideration.
• The request for reconsideration
must contain a certification in
substantially the same form as that
provided by 50 CFR 13.12(a)(5). If a
request for reconsideration does not
contain that certification, but is
otherwise timely and appropriate, the
Service will hold the request and give
the person submitting the request
written notice of the need to submit the
certification within 15 calendar days.
Failure to submit certification will
result in the Service rejecting the
request as insufficient in form and
content.
(10) (NEW—Existing In Use Without
OMB Approval) Compensatory
Mitigation (§ 22.220)—Any permit
authorizing take that would exceed the
applicable EMU take limit will require
compensatory mitigation, except in
circumstances where the action is
considered in the best interest of an
eagle. Compensatory mitigation for this
purpose must ensure the preservation of
the affected eagle species by mitigating
an amount equal to or greater than the
authorized or expected take.
Compensatory mitigation must either
reduce another ongoing form of
mortality or increase the eagle
population of the affected species.
Compensatory mitigation for golden
eagles must be performed at a 1.2:1
(mitigation: take) ratio. A permit may
require compensatory mitigation when
the Service determines, according to the
best available information, that the take
authorized by the permitted activity is
not consistent with maintaining the
persistence of the local area population
of an eagle species.
The Service must approve types of
compensatory mitigation and may
include conservation banks, in-lieu fee
programs, or permittee-responsible
mitigation as mitigation providers.
General permittees meet this
requirement by obtaining required
credits from a Service-approved, thirdparty mitigation provider. Specific
permittees can meet this requirement by
obtaining required credits from a
Service-approved, third-party mitigation
provider or meeting the requirements to
be a permittee-responsible mitigation
provider as described in 50 CFR
22.220(c)(2). Third-party mitigation
providers, such as in-lieu fee programs
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and conservation banks, obtain Service
approval by meeting the requirements to
be a mitigation provider as described in
50 CFR 22.220(c)(2).
To obtain approval as a mitigation
provider, potential providers must
submit a mitigation plan to the Service
that demonstrates how the standards in
50 CFR 22.220(b) will be met. At a
minimum, this must include a
description of the mitigation, the benefit
to eagles, the locations where projects
will be implemented, the EMU and local
area population affected, the number of
credits provided, and an explanation of
the rationale for the number of eagle
credits provided. The Service must
approve the mitigation plan prior to
implementation.
(11) (NEW—Existing In Use Without
OMB Approval) Single Application for
Multiple Activities (50 CFR
13.11(d)(1))—If regulations require more
than one type of permit for an activity
and permits are issued by the same
office, the issuing office may issue one
consolidated permit. Applicants may
submit a single application in these
cases, provided the single application
contains all the information required by
the separate applications for each
permitted activity. In instances where
the Service consolidates more than one
permitted activity into one permit, the
issuing office will charge the highest
single fee for the activity permitted.
Administration fees are not waived for
single applications covering multiple
activities.
We have renewed the existing
reporting and recordkeeping
requirements identified below:
(1) Form 3–200–14, ‘‘Eagle
Exhibition’’—This form is used to apply
for a permit to possess and use eagles
and eagle specimens for educational
purposes. In addition to the
standardized information required by 50
CFR 13.12, permit application
requirements include submission of the
following information: type of eagle(s)
or eagle specimens; status of other
required authorizations (State, Tribal,
local); description of the programs that
will be offered and how the eagles will
be displayed; experience of handlers;
and information about enclosures, diet,
and enrichment for the eagles. The
Service uses the information collected
via the form to determine whether the
eagles are legally acquired and will be
used for bona fide conservation
education, and in the case of live eagles,
will be housed and handled under safe
and healthy conditions.
(2) Form 3–200–15a, ‘‘Eagle Parts for
Native American Religious Purposes’’—
This application form is used by
enrolled members of federally
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recognized Tribes to obtain
authorization to acquire and possess
eagle feathers and parts from the
Service’s National Eagle Repository
(NER). The permittee also uses the form
to make additional requests for eagle
parts and feathers from the NER. The
form collects the following information:
name of the Tribe; Tribal enrollment
number of the individual applicant; a
signed Certification of Enrollment;
inmate-specific information in cases
where applicants are incarcerated
(inmate number, institution, contact
information for the institute’s chaplain);
and the specific eagle parts and/or
feathers desired by the applicant. The
Service uses the information collected
via the form to verify that the applicant
is an enrolled member of a federally
recognized Tribe, and what parts and/or
feathers the applicant is requesting.
(3) Form 3–200–16, ‘‘Take of
Depredating Eagles & Eagles that Pose a
Risk to Human or Eagle Health or
Safety—Annual Report’’—Applicants
use this form to obtain authorization to
take (trap, collect, haze) eagles that
depredate on wildlife or livestock, as
well as eagles situated where they pose
a threat to human or their own safety.
In addition to the standardized
information required by 50 CFR 13.12,
permit application requirements include
submission of the following
information: status of other required
authorizations (State, Tribal, local); the
species and estimated number of eagles
causing the problem; what the damage
or risk consists of; location; method of
take; alternatives taken that were not
effective; and a description of the
proposed long-term remedy. The
Service uses the information collected
via the form to determine whether the
take is necessary to protect the relevant
interests; other alternatives have been
considered; and the method of take is
humane and compatible with the
preservation of eagles.
(4) Form 3–200–18, ‘‘Take of Golden
Eagle Nests During Resource
Development or Recovery’’—This
application is used by commercial
entities engaged in resource
development or recovery operations,
such as mining or drilling, to obtain
authorization to remove or destroy
golden eagle nests. In addition to the
standardized information required by 50
CFR 13.12, permit application
requirements include submission of the
following information: location of the
property; the status of other required
authorizations; the type of development
or recovery operation; the number of
nests to be taken; the activity that
involves the take of the nest; the
disposition of the nests once removed
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(or destroyed); the duration for which
the authorization is requested; and a
description of the mitigation measures
that will be implemented. The Service
uses the information collected via the
form to determine whether the take is
necessary and will be compatible with
the preservation of eagles.
(5) Form 3–200–77, ‘‘Native American
Eagle Take for Religious Purposes’’—
Federally recognized Native American
Tribes use this form to apply for
authorization to take eagles from the
wild for Tribal religious purposes. In
addition to the standardized
information required by 50 CFR 13.12,
permit application requirements include
submission of the following
information: status of other required
authorizations; location of proposed
take; statement of consent by the land
owner or land manager if not on Tribal
land; species, number, and age class of
eagles; whether the eagles will be
collected alive and held in captivity;
intended disposition of parts and
feathers; and the reason why eagles
obtained by other means do not meet
the Tribe’s religious needs. The Service
uses the information obtained via the
form to determine whether the take is
necessary to meet the Tribe’s religious
needs, they received consent of the
landowner, the take is compatible with
the preservation of eagles, and any
eagles kept alive will be held under
humane conditions.
(6) Form 3–200–78, ‘‘Native American
Tribal Eagle Aviary’’—Federally
recognized Native American Tribes use
this form to apply for authorization to
keep live eagles for Tribal religious
purposes. In addition to the
standardized information required by 50
CFR 13.12, permit application
requirements include submission of the
following information: descriptions,
photographs and/or diagrams of the
enclosures where the eagles will be
housed, and number of eagles that will
be kept in each; status of other required
authorizations; names and eaglehandling experience of caretakers;
veterinarian who will provide medical
care; and description of the diet and
enrichment the Tribe will provide the
eagles. The Service uses the information
collected via the form to ensure the
Tribe has the appropriate facilities and
experience to keep live eagles safely and
humanely.
(7) Form 3–200–82, ‘‘Bald Eagle or
Golden Eagle Transport into the United
States for Scientific or Exhibition
Purposes’’—This application is used by
researchers and museums to obtain
authorization to temporarily bring eagle
specimens into, or take those specimens
out of, the United States. In addition to
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the standardized information required
by 50 CFR 13.12, permit application
requirements include submission of the
following information: documentation
that the specimen was legally obtained;
documentation that the applicant meets
the definition of a ‘‘public’’ institution
as required under statute; status of other
required authorizations (State, Tribal,
local); description of the specimen(s);
country of origin; name of and contact
information for the foreign institution;
scientific or exhibition purposes for the
transport of specimens; locations where
the item will be exhibited (if
applicable); dates and ports of
departure/arrival; and names of persons
acting as agents for the applicant. The
Service uses the information collected
via the form to ensure the specimens
were legally acquired and will be
transported through U.S. ports that can
legally authorize the transport, the
transport will be temporary, as required
by statute, and the specimens will be
used for purposes authorized by statute.
(8) Form 3–1552 ‘‘Native American
Tribal Eagle Retention’’—A Federal
Eagle Remains Tribal Use permit
authorizes a federally recognized Tribe
to acquire, possess, and distribute to
Tribal members whole eagle remains
found by a Tribal member or employee
on the Tribe’s Tribal land for Indian
religious use. The applicant must be a
federally recognized Tribal entity under
the Federally Recognized Tribal List Act
of 1994, 25 U.S.C. 479a–1, 108 Stat.
4791 (1994). In addition to the
standardized information required by 50
CFR 13.12, the form also collects the
following information: name of the
Tribe; name and contact information for
the Tribal leader and primary contact
person; whether the Tribe has already
discovered an eagle to hold under the
permit; and if different than what’s
listed for the primary contact, the
address of the physical location where
records will be kept. The Service uses
the information collected via the form to
identify which Tribe is applying for the
permit and to inform the Service as to
whether the Tribe is applying before or
subsequent to finding the first eagle they
want to retain, allowing the Service to
choose the appropriate course of action.
(9) Form 3–1591, ‘‘Tribal Eagle
Retention—Acquisition Form’’—This
form provides the Service information
needed to track the chain of custody of
eagle remains and ensure the Tribe takes
possession of them as authorized under
the permit. The first part of the form
(completed by a Service Office of Law
Enforcement (OLE) Officer) collects:
species; sex; age class of eagle; date and
location discovered; date the
information was reported to track eagle
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mortalities; date the remains were
transferred to the Tribe; name and
contact information for the Tribe; and
OLE officer name and contact
information. The second part of the
form (competed by the Tribe) collects:
permit number; date the Tribe took
possession of the eagle; and Principal
Tribal Officer’s name, title, and contact
information.
(10) Form 3–2480, ‘‘Eagle Recovery
Tag’’—The form is used to track dead
eagles as they move through the process
of laboratory examination to determine
cause of death and are sent to the NER
for distribution to Native Americans for
use in religious ceremonies. In addition
to the standardized information
required by 50 CFR 13.12, the form also
collects the following information: U.S.
Geological Survey band data; unique ID
number assigned; mortality date;
species, age, and sex of the eagle; date
recovered; name of person(s) who found
and recovered the eagle; and names and
contact information of persons who
received the eagle throughout the chain
of custody. The Service uses the
information collected to maintain chain
of custody for law enforcement and
scientific purposes.
(11) Form 3–202–11, ‘‘Take of
Depredating Eagles & Eagles that Pose a
Risk to Human or Eagle Health or
Safety—Annual Report’’—Permittees
use this form to report the outcome of
their action involving take of
depredating eagles or eagles that pose a
risk to human or eagle health or safety.
The form collects the following
information: species, location, date of
take, number of eagles, method of take,
and final disposition. The Service uses
the information reported via the form to
ascertain whether the planned take was
implemented, track how much
authorized take occurred in the eagle
management unit and local population
area, and verify the disposition of any
eagles taken under the permit.
(12) Form 3–202–13, ‘‘Eagle
Exhibition—Annual Report’’—
Permittees use this form to report
activities conducted under an Eagle
Exhibition Permit for both Live and
Dead Eagles. The form collects the
following information: list of eagles and
eagle specimens held under the permit
during the reporting year, and, for each,
the date acquired or disposed of; from
whom acquired or to whom transferred;
total number of programs each eagle was
used in, or if statically displayed (e.g.,
in a museum setting), the number of
days the facility was open to the public.
The Service uses the information
reported through this form to verify that
eagles held under the permit are used
for conservation education.
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(13) Form 3–202–14, ‘‘Native
American Tribal Eagle Aviary—Annual
Report’’—Permittees use this form to
report activities conducted under a
Native American Eagle Aviary Permit.
The form collects the following
information: a list of eagles held under
the permit during the reporting year,
and, for each, the date acquired or
disposed of; from whom acquired or to
whom transferred; or other disposition.
The Service uses the information
collected via the form to track the live
eagles held by federally recognized
Tribes for spiritual and cultural
practices.
(14) Monitoring Requirements—Most
permits that authorize take of eagles or
eagle nests require monitoring. We do
not require monitoring for intentional
take, including when Native American
Tribes take an eagle as part of a religious
ceremony or when falconers trap golden
eagles that are depredating on livestock.
A fundamental purpose of monitoring
under eagle take permits is to track
levels of take for population
management. For disturbance permits,
monitoring also provides information
about whether the permitted activity
actually disturbed eagles, allowing the
Service to better understand when these
types of permits may not be needed.
In addition to tracking take at
population management scales, the
Service uses data from monitoring lethal
take permits to adjust authorized take
levels, compensatory mitigation
requirements, and avoidance and
minimization measures as spelled out
under the terms of the permit. With
regard to wind industry permits, these
data also enable the Service to improve
future fatality estimates through
enhanced understanding of exposure
and collision.
(15) Required Notifications—Most
permits that authorize take or
possession of eagles require a timely
notification to the Service by email or
phone when an eagle possessed under a
possession permit or taken under a
permit to take eagles dies or is found
dead. These fatalities are later recorded
in reports submitted to the Service as
described above. The timely
notifications allow the Service to better
track take and possession levels, and to
ensure eagle remains are sent to either
a forensics lab or the NER. Incidental
take permittees are also required to
notify the Service via email or phone if
a threatened or endangered species is
found in the vicinity of the activity for
which take is permitted. There is no
notification requirement for that beyond
reporting each occurrence where take is
discovered to have occurred. The
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Service tracks whether the take level is
exceeded or is likely to be exceeded.
(16) Recordkeeping Requirements—
As required by 50 CFR 13.46, permittees
must keep records of the activity as it
relates to eagles and any data gathered
through surveys and monitoring,
including records associated with the
required internal incident reporting
system for bald eagle and golden eagle
remains found and the disposition of
the remains. This information retained
by permittees is described above under
reporting requirements.
(17) Amendments—Amendments to a
permit may be requested by the
permittee, or the Service may amend a
permit for just cause upon a written
finding of necessity. Amendments
comprise changes to the permit
authorization or conditions. Those
changes may include an increase or
decrease in the authorized take or
possession of eagles, proposed
adjustment of permit conditions, or
changes to the activity involving eagles.
The permit will specify circumstances
under which the Service will require
modifications to avoidance,
minimization, or compensatory
mitigation measures or monitoring
protocols, which may include, but are
not limited to take levels, location of
take, and/or changes in eagle use of the
activity area.
At a minimum, the permit must
specify actions to be taken if take
approaches or reaches the amount
authorized and anticipated within a
given timeframe. The permittee applies
for amendments to the permit by
submitting a description of the modified
activity and the changed conditions
affecting eagles. Substantive
amendments incur a processing fee. A
permittee is not required to pay a
processing fee for minor changes, such
as the legal individual or business name
or mailing address of the permittee. A
permittee is required to notify the
issuing office within 10 calendar days of
minor changes.
(18) Transfers—In general, permits
issued under 50 CFR part 22 are not
transferable. However, when authorized,
permits issued under § 22.80 may be
transferred by the transferee providing
written assurances of sufficient funding
of the avoidance and minimization
measures and commitment to carry out
the terms and conditions of the permit.
Copies of the draft forms are available
to the public by submitting a request to
the Service Information Collection
Clearance Officer using one of the
methods identified in ADDRESSES.
Title of Collection: Eagle Permits and
Fees, 50 CFR parts 10, 13, and 22.
OMB Control Number: 1018–0167.
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Form Numbers: FWS Forms 3–200–
14, 3–200–15a, 3–200–16, 3–200–18, 3–
200–71, 3–200–72, 3–200–77, 3–200–78,
3–200–82, 3–202–11, 3–202–13, 3–202–
14, 3–202–15, 3–202–16, 3–1552, 3–
1591, 3–2480, 3–202–91 (New).
Type of Review: Revision of a
currently approved collection.
Respondents/Affected Public:
Individuals, businesses, and State/local/
Tribal governments. We expect the
majority of applicants seeking permits
will be in the energy production and
electrical distribution business.
Total Estimated Number of Annual
Respondents: 8,406.
Total Estimated Number of Annual
Responses: 8,406.
Estimated Completion Time per
Response: Varies from 15 minutes to
200 hours, depending on activity.
Total Estimated Number of Annual
Burden Hours: 32,882.
Respondent’s Obligation: Required to
obtain or retain a benefit.
Frequency of Collection: On occasion
for applications; annually or on
occasion for reports.
Total Estimated Annual Non-hour
Burden Cost: $1,737,460 (primarily
associated with application processing
and administrative fees).
On September 30, 2022, we published
in the Federal Register (87 FR 59598) a
proposed rule (RIN 1018–BE70) that
announced our intention to request
OMB approval of the revisions to this
collection explained above and the
simultaneous renewal of OMB Control
No. 1018–0167. In that proposed rule,
we solicited comments for 60 days on
the information collections in this
submission, ending on November 29,
2022. Summaries of comments
addressing the information collections
contained in this rule, as well as the
agency response to those comments, can
be found in the Response to Public
Comments section of this rule, as well
as in the information collection request
submitted to OMB on the RegInfo.gov
website (https://www.reginfo.gov/
public/).
As part of our continuing effort to
reduce paperwork and respondent
burdens, we invite the public and other
Federal agencies to comment on any
aspect of this information collection,
including:
(1) Whether or not the collection of
information is necessary for the proper
performance of the functions of the
agency, including whether or not the
information will have practical utility;
(2) The accuracy of our estimate of the
burden for this collection of
information, including the validity of
the methodology and assumptions used;
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9955
(3) Ways to enhance the quality,
utility, and clarity of the information to
be collected; and
(4) How the agency might minimize
the burden of the collection of
information on those who are to
respond, including through the use of
appropriate automated, electronic,
mechanical, or other technological
collection techniques or other forms of
information technology, e.g., permitting
electronic submission of response.
Send your written comments and
suggestions on this information
collection by the date indicated in
DATES to https://www.reginfo.gov/
public/do/PRAMain. Find this
particular information collection by
selecting ‘‘Currently under 30-day
Review—Open for Public Comments’’ or
by using the search function. Please
provide a copy of your comments to the
Service Information Collection
Clearance Officer, U.S. Fish and
Wildlife Service, MS: PRB/PERMA
(JAO), 5275 Leesburg Pike, Falls
Church, VA 22041–3803 (mail); or by
email to Info_Coll@fws.gov. Please
reference OMB Control Number 1018–
0167 in the subject line of your
comments.
National Environmental Policy Act (42
U.S.C. 4321 et seq.)
We evaluated the environmental
impacts of the changes to the
regulations and completed an
environmental assessment and finding
of no significant impact. The FONSI is
the final step in the NEPA process for
this eagle rule revision process. The
FONSI and final environmental
assessment are available in Docket No.
FWS–HQ–MB–2020–0023 (available at
https://www.regulations.gov).
Endangered and Threatened Species
Section 7 of the Endangered Species
Act of 1973, as amended (16 U.S.C.
1531–43), requires Federal agencies to
‘‘ensure that any action authorized,
funded, or carried out . . . is not likely
to jeopardize the continued existence of
any endangered species or threatened
species or result in the destruction or
adverse modification of [critical]
habitat’’ (16 U.S.C. 1536(a)(2)). IntraService consultations and conferences
consider the effects of the Service’s
actions on listed species, species
proposed for listing, and candidate
species. Our final action of issuing our
regulations regarding take of non-ESAlisted eagles does not authorize, fund, or
carry out any activity that may affect—
directly or indirectly—any ESA-listed
species or their critical habitat. See, e.g.,
Sierra Club v. Bureau of Land Mgmt.,
786 F.3d 1219 (9th Cir. 2015). Indeed,
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the Eagle Act does not empower us to
authorize, fund, or carry out project
activities by third parties. The Eagle Act
empowers us to authorize take of bald
and golden eagles. Thus, we have
determined these revisions have no
effect on any listed species, species
proposed for listing, or candidate
species or their critical habitat. As a
result, section 7 consultation is not
required on this rulemaking action. As
appropriate, we will conduct projectspecific, intra-Service section 7
consultations in the future if our
proposed act of issuing a permit for take
of eagles may affect ESA-listed species
or critical habitat.
Government-to-Government
Relationship With Tribes
In accordance with the President’s
memorandum of April 29, 1994,
‘‘Government-to-Government Relations
with Native American Tribal
Governments’’ (59 FR 22951), E.O.
13175, and the Department of the
Interior’s manual at 512 DM 2, we
readily acknowledge our responsibility
to communicate meaningfully with
recognized Federal Tribes on a
government-to-government basis. In
accordance with Secretary’s Order 3206
of June 5, 1997 (American Indian Tribal
Rights, Federal-Tribal Trust
Responsibilities, and the Endangered
Species Act), we readily acknowledge
our responsibilities to work directly
with Tribes in developing programs for
healthy ecosystems, to acknowledge that
Tribal lands are not subject to the same
controls as Federal public lands, to
remain sensitive to Indian culture, and
to make information available to Tribes.
Although we do not consider this
rulemaking as having Tribal
implications according to E.O. 13175
because it is not likely to have
‘‘substantial direct effects’’ on any
particular Tribe, we conducted Tribal
outreach and invited government-togovernment consultation as if it does.
The Service provided written
notification to Tribes about the ANPR
and the proposed rule and offered
government-to-government
consultation. The Service conducted
Tribal informational webinars on
October 14 and 21, 2021, during the
ANPR public comment period as well as
prior to publication of the proposed
rule. Seven Tribal representatives
provided written comments. The
Service conducted two additional Tribal
informational webinars on October 19
and November 2, 2022, during the
proposed rule public comment period as
well as bilateral information sessions
when requested by Tribes. Tribal
consulation was requested by one Tribe,
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which was conducted in September
2023. No other Tribes requested
consultation with the Service. The
Service conducted a final Tribal
informational webinar on December 12,
2023, regarding the changes the Service
made in developing the final rule.
Eleven Tribal representatives provided
written comments. As described earlier
in this preamble, we have revised the
proposed regulations in response to
these comments.
The Service acknowledges our
Federal Tribal trust responsibilities and
deeply honors our sovereign nation-tonation relationship with Tribes.
Throughout all phases of the rulemaking
process, the Service has encouraged and
welcomed Tribal engagement, including
government-to-government
consultation. To date, we have
conducted one government-togovernment consultation. We invite
further bilateral government-togovernment consultation at any time.
Energy Supply, Distribution, or Use
(E.O. 13211)
E.O. 13211 requires agencies to
prepare statements of energy effects
when undertaking certain actions. This
rule is a significant regulatory action
under E.O. 12866; however, it will not
significantly affect energy supplies,
distribution, or use. The permitting
process streamlines permitting for wind
energy and power distribution;
therefore, the rule is intended to ease
any administrative burden on energy
development and will not impact it
negatively. Therefore, this action is not
a significant energy action, and no
statement of energy effects is required.
List of Subjects
50 CFR Part 13
Administrative practice and
procedure, Exports, Fish, Imports,
Plants, Reporting and recordkeeping
requirements, Transportation, Wildlife.
50 CFR Part 22
Exports, Imports, Reporting and
recordkeeping requirements,
Transportation, Wildlife.
Regulation Promulgation
Accordingly, we hereby amend parts
13 and 22 of subchapter B of chapter I,
title 50 of the Code of Federal
Regulations, as set forth below:
PART 13—GENERAL PERMIT
PROCEDURES
1. The authority citation for part 13
continues to read as follows:
■
Authority: 16 U.S.C. 668a, 704, 712, 742j–
l, 1374(g), 1382, 1538(d), 1539, 1540(f), 3374,
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4901–4916; 18 U.S.C. 42; 19 U.S.C. 1202; 31
U.S.C. 9701.
■
2. Revise § 13.5 to read as follows:
§ 13.5
Information collection requirements.
The Office of Management and Budget
(OMB) has approved the information
collection requirements contained in
part 13 and assigned OMB Control
Numbers 1018–0022, 1018–0070, 1018–
0092, 1018–0093, or 1018–0167 (unless
otherwise indicated). Federal agencies
may not conduct or sponsor, and a
person is not required to respond to, a
collection of information unless it
displays a currently valid OMB control
number. Direct comments regarding the
burden estimates or any other aspect of
the information collection to the
Service’s Information Collection
Clearance Officer at the address
provided at 50 CFR 2.1(b).
■ 3. Amend § 13.11 by:
■ a. Revising paragraphs (d)(2) and
(d)(3)(i); and
■ b. In the table in paragraph (d)(4):
■ i. Removing the 15 entries under
‘‘Bald and Golden Eagle Protection Act’’
and adding 17 new entries in their
place; and
■ ii. Revising the footnote 1.
The revisions and additions read as
follows:
§ 13.11
Application procedures.
*
*
*
*
*
(d) * * *
(2) If regulations in this subchapter
require more than one type of permit for
an activity and the permits are issued by
the same office, the issuing office may
issue one consolidated permit
authorizing take caused by the activity
in accordance with § 13.1. You may
submit a single application in these
cases, provided that the single
application contains all the information
required by the separate applications for
each activity. Where more than one
activity is consolidated into one permit,
the issuing office will charge the highest
single fee for the activity for which take
is permitted. Administration fees are not
waived.
(3) * * *
(i) We will not charge a permit
application fee to any Federal, Tribal,
State, or local government agency or to
any individual or institution acting on
behalf of that agency, except
administration fees for permits issued
under subpart E of part 22 of this
subchapter will not be waived. If you
fail to submit evidence of agency status
with your application, we will require
the submission of all processing fees
prior to the acceptance of the
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application for processing, unless
otherwise authorized or waived.
*
*
*
*
*
(4) * * *
Type of permit
*
Permit application fee 1
CFR citation
*
*
*
Administration fee 2
*
Amendment fee
*
*
Bald and Golden Eagle Protection Act
Eagle Scientific Collecting ..............................
Eagle Exhibition ..............................................
Eagle—Native American Religious Purposes
Eagle Depredation Permit ...............................
Golden Eagle Nest Take ................................
Eagle Transport—Scientific or Exhibition .......
Eagle Transport—Native American Religious
Purposes.
General Eagle Permit—Disturbance Take .....
Specific Eagle Permit—Disturbance Take ......
50
50
50
50
50
50
50
.......
.......
.......
.......
.......
.......
.......
100.
75.
No fee.
100.
100 .........................................
75.
No fee.
50 CFR part 22 .......
50 CFR part 22 .......
50 CFR part 22 .......
100.
Commercial—2,500; Noncommercial—500.
100.
Commercial—2,500; Noncommercial—500.
5,000 ......................................
General Eagle Permit—Nest Take .................
Specific Eagle Permit—Nest Take (Single
nest).
Specific Eagle Permit Eagle—Nest Take
(Multiple nests).
General Eagle Permit—Incidental Take
(Power lines).
General Eagle Permit—Incidental Take (Wind
energy).
50 CFR part 22 .......
50 CFR part 22 .......
50 CFR part 22 .......
1,000 ......................................
50 CFR part 22 .......
1,000 ......................................
Specific Eagle Permit—Incidental Take .........
50 CFR part 22 .......
Eagle Take—Exempted under ESA ...............
Transfer of a Subpart E Eagle Permit ............
50 CFR part 22 .......
50 CFR part 22 .......
Tier 1—18,000; Tier 2—
26,000.
................................................
1,000.
*
1A
CFR
CFR
CFR
CFR
CFR
CFR
CFR
part
part
part
part
part
part
part
*
22
22
22
22
22
22
22
*
*
................................................
50.
................................................
Commercial—500; Noncommercial—150.
................................................
................................................
Commercial—500; Noncommercial—150.
500.
Non-Investor Owned—2,500;
Investor Owned—10,000.
Distributed and Community
Scale—2,500; Utility
Scale—10,000.
10,000 ....................................
500.
No fee.
*
*
*
reimbursable agreement may be required for specific eagle permits to cover the costs above estimated staff-hours.
administration fee will be assessed at the time of application, in addition to the application fee.
2 An
*
*
*
*
The revisions and additions read as
follows:
*
4. Amend § 13.12 by:
a. Revising paragraph (a)(1)(ii); and
■ b. In table 1 to paragraph (b),
removing the 8 entries under ‘‘Eagle
Permits’’ and adding in their place 10
new entries.
■
§ 13.12 General information requirements
on applications for permits.
■
(a) * * *
(1) * * *
(ii) If the applicant is an individual,
the date of birth, occupation, and any
business, agency, organizational, or
institutional affiliation associated with
the wildlife or plants to be covered by
the license or permit; or
*
*
*
*
*
(b) * * *
TABLE 1 TO PARAGRAPH (b)
Type of permit
Section
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*
*
*
*
*
*
Eagle permits:
Scientific or exhibition .......................................................................................................................................................
Indian religious use ..........................................................................................................................................................
Falconry purposes ............................................................................................................................................................
Depredation and protection of health and safety .............................................................................................................
Permits for incidental take of eagles ................................................................................................................................
Permits for incidental take of eagles by power lines .......................................................................................................
Permits for disturbance take of eagles .............................................................................................................................
Permits for nest take of eagle ..........................................................................................................................................
Permits for golden eagle nest take for resource recovery operations .............................................................................
Permits for bald eagle take exempted under the Endangered Species Act ....................................................................
§ 13.24
[Amended]
§ 13.25
5. Amend § 13.24 in paragraph (c)
introductory text by removing ‘‘§ 22.80
of this subchapter B’’ and adding in its
place ‘‘part 22, subpart E, of this
subchapter’’.
■
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[Amended]
6. Amend § 13.25 in paragraphs (b)
introductory text and (f) by removing
‘‘§ 22.80 of this subchapter B’’ and
adding in its place ‘‘part 22, subpart E,
of this subchapter’’.
Frm 00039
Fmt 4701
22.50.
22.60.
22.70.
22.100.
22.200 or
22.200 or
22.200 or
22.200 or
22.325.
22.400.
22.210.
22.210.
22.210.
22.210.
PART 22—EAGLE PERMITS
■
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7. The authority citation for part 22
continues to read as follows:
■
Authority: 16 U.S.C. 668–668d; 703–712;
1531–1544.
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8. Amend § 22.6 by:
a. Revising the definitions of ‘‘Eagle
management unit (EMU)’’ and ‘‘Eagle
nest’’;
■ b. Adding in alphabetic order a
definition for ‘‘General permit’’;
■ c. Revising the definition of ‘‘In-use
nest’’; and
■ d. Adding in alphabetic order a
definition of ‘‘Incidental take’’.
The revisions and additions read as
follows:
■
■
§ 22.6
Definitions.
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*
*
*
*
*
Eagle management unit (EMU) means
a geographically bounded region within
which permitted take is regulated to
meet the management goal of
maintaining stable or increasing
breeding populations of bald eagles or
golden eagles.
(1) The Atlantic EMU is Connecticut,
Delaware, Florida, Georgia, Maine,
Maryland, Massachusetts, New
Hampshire, New Jersey, New York,
North Carolina, Pennsylvania, Rhode
Island, South Carolina, Vermont,
Virginia, and West Virginia.
(2) The Mississippi EMU is Alabama,
Arkansas, Illinois, Indiana, Iowa,
Kentucky, Louisiana, Michigan,
Minnesota, Mississippi, Missouri, Ohio,
Tennessee, and Wisconsin.
(3) The Central EMU is Kansas,
Nebraska, New Mexico, North Dakota,
Oklahoma, South Dakota, and Texas;
portions of Colorado, New Mexico, and
Wyoming east of the Continental Divide;
and portions of Montana east of Hill,
Chouteau, Cascade, Meagher, and Park
Counties.
(4) The Pacific EMU is Alaska,
Arizona, California, Idaho, Nevada,
Oregon, Utah, Washington; portions of
Colorado, New Mexico, and Wyoming
west of the Continental Divide; and in
Montana Hill, Chouteau, Cascade,
Meagher, and Park Counties and all
counties west of those counties.
(5) An EMU may be further divided
between north and south along the 40th
Parallel.
Eagle nest means any assemblage of
materials built, maintained, or used by
bald eagles or golden eagles for the
purpose of reproduction. An eagle nest
remains an eagle nest until it becomes
so diminished, or the nest substrate
upon which it is built fails, that the nest
is no longer usable and is not likely to
become usable to eagles, as determined
by a Federal, Tribal, or State eagle
biologist.
*
*
*
*
*
General permit means a permit that
has nationwide or regional standard
conditions for a category, or categories,
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of activities that are substantially
similar in nature.
*
*
*
*
*
In-use nest means a bald eagle or
golden eagle nest that contains one or
more viable eggs or dependent young,
or, for golden eagles only, has had adult
eagles on the nest within the past 10
days during the breeding season.
Incidental take means take that is
foreseeable and results from, but is not
the purpose of, an activity.
*
*
*
*
*
■ 9. Amend § 22.12 by adding paragraph
(c) to read as follows:
§ 22.12
Illegal activities.
*
*
*
*
*
(c) Application for a permit does not
release you from liability for any take
that occurs prior to issuance of, or
outside the terms of, a permit.
■ 10. Revise the heading of subpart C to
read as follows:
Subpart C—Eagle Possession Permit
Provisions
§ 22.80
■
§ 22.85
■
■
[Removed and Reserved]
11. Remove and reserve § 22.80.
[Removed and Reserved]
12. Remove and reserve § 22.85.
13. Add subpart E to read as follows:
Subpart E—Take of Eagles for Other
Interests
Sec.
22.200 Specific permits.
22.210 General permits.
22.215 Conditions of permits.
22.220 Compensatory mitigation.
22.250 Permits for incidental take of eagles
by wind energy projects.
22.260 Permits for incidental take of eagles
by power lines.
22.280 Permits for disturbance take of
eagles.
22.300 Permits for take of eagle nests.
§ 22.200
Specific permits.
(a) Purpose. Specific permits
authorize the take of bald eagles or
golden eagles for other interests by
activities that are described in the
regulations in this subpart. Proponents
of projects may apply for a specific
permit if they do not meet eligibility
criteria for general permits described
in—or are conducting an activity not
identified in—§ 22.250, § 22.260,
§ 22.280, or § 22.300. Specific permits
may be recommended by the Service or
requested by entities that are eligible for
but do not want to obtain a general
permit.
(b) Eligibility. To qualify for a specific
permit, you must be conducting an
activity identified in § 22.250, § 22.260,
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§ 22.280, or § 22.300. You must also
meet any eligibility requirements
identified in the relevant section.
(1) Permits are issued to the
individual or entity conducting the
activity, such as the owner or manager
of the entity conducting the activity.
The applicant is responsible for
compliance with the permit and must
have the authority to implement the
required permit conditions.
(2) Contractors or consultants may
assist in completing applications or
conducting work as a subpermittee but
may not be a permit holder.
(3) Applicants may not break down a
project into small parts to minimize the
activity.
(4) Applicants may not combine
projects if the activities are not readily
identifiable as being part of the same
project. If you want to obtain a
consolidated permit for multiple
activities, you must first submit a
separate application for each project and
request the Service determine if it is
appropriate to consolidate permits.
(5) Specific permits are issued to a
single permit holder. If multiple entities
operate a joint project and want to
obtain joint authorization, the
application must designate one entity as
the permit holder and that entity must
accept the legal liability for the other
entities. The other entities must grant
sufficient authority to the permit holder
to carry out any activities required
under the permit.
(6) Upon receipt of your application
for a specific permit, the Service may
direct you to apply for a general permit
or determine that a permit is not
required. The Service will provide a
letter of authorization to keep in your
records.
(7) For existing wind energy projects
only, projects that are not eligible for a
general permit for incidental take of
eagles (§ 22.250) may request a Letter of
Authorization from the Service to apply
for a general permit. The Service will
review and determine if eagle risk at the
project is consistent with the risk
expected for general permits. To request
review, you must submit a specific
permit application and request a
determination for general permit
eligibility. Your administration fee will
not be refunded to cover the cost of
conducting this review. The application
fee may be refunded (50 CFR
13.11(d)(1)).
(c) How to apply for a specific permit.
(1) Submit a completed application form
as specified in § 22.250(a), § 22.260(a),
§ 22.280(a), or § 22.300(a), as applicable,
or Form 3–200–71 if the activity does
not correspond with a particular permit
type. Submit forms to the Regional
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Director of the region where you will
conduct your activity. If your activity
spans multiple regions, submit your
application to the region of your U.S.
mailing address, and the Service will
assign the appropriate administering
region. You can find the current contact
information for Regional Directors in
§ 2.2 of subchapter A of this chapter.
(2) Your application must include:
(i) A description of the activity that
will cause the take to be authorized,
including the location, seasonality, and
duration of the activity.
(A) If applying under § 22.250 for
wind energy projects, that description
must include the number of turbines,
rotor diameter, hub height, location
coordinates of each turbine, and the
datum of these coordinates.
(B) If applying under § 22.260 for
power lines, include the State and
county(ies) of coverage and total miles
of transmission and distribution lines.
To the extent known, include the
number of miles or number of poles in
eagle-risk areas that are not avian-safe.
(C) If applying under § 22.280 or
§ 22.300, include the location of known
nest(s) and nest status (e.g., in-use or
alternate).
(ii) Justification of why there is no
practicable alternative to take that
would protect the interest to be served.
(iii) An eagle impacts assessment,
including eagle activity and eagle use in
the project area and a description of
methods used to conduct this
assessment. If the Service has officially
issued or endorsed survey, modeling,
take-estimation, or other standards for
the activity that will take eagles, you
must follow them and include in your
application all the information thereby
obtained, unless the Service waives this
requirement for your application.
(iv) Implemented and proposed steps
to avoid and minimize to the maximum
degree practicable, compensate for, and
monitor impacts on eagles.
(v) Alternative actions considered and
the reasons why those alternatives are
not practicable.
(vi) Any supplemental information
necessary for the Service to make an
adequate determination on the
application (see § 13.21 of this
subchapter).
(vii) Payment of the required
application and administration fees (see
§ 13.11(d)(4) of this subchapter) for the
appropriate fee tier, and, if required,
proposed compensatory mitigation plan
or eagle credits to be obtained from a
Service-approved conservation bank or
in-lieu fee program. All compensatory
mitigation must comply with the
provisions of § 22.220. For incidental
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take permits issued under §§ 22.250 and
22.260:
(A) The Tier 1 application fee is
assessed when standardized permit
conditions require negligible
modifications, additional environmental
compliance review is not required, and,
if required, fatality estimates require
minimal data manipulation.
(B) The Tier 2 application fee is
assessed for all other specific permit
incidental take applications that require
275 staff-hours or fewer for review,
including compliance with the
procedural requirements of NEPA. The
Service may require applicants to enter
into a reimbursable agreement to cover
the costs above 275 staff-hours.
(d) Issuance criteria. Upon receiving a
complete application, the Regional
Director will decide whether to issue a
permit based on the general criteria of
§ 13.21 of this subchapter and whether
the application meets the following
requirements:
(1) The applicant is eligible for a
specific permit.
(2) The take:
(i) Is necessary to protect a legitimate
interest in a particular locality;
(ii) Results from, but is not the
purpose of, the activity; and
(iii) Cannot practicably be avoided.
(3) The amount of take the Service
authorizes under the permit is
compatible with the preservation of the
bald eagle and the golden eagle,
including consideration of the effects of
other permitted take and other factors
affecting bald eagle and golden eagle
populations.
(4) The applicant has proposed
avoidance and minimization measures
to reduce the take to the maximum
degree practicable relative to the
magnitude of the activity’s impacts on
eagles. These measures must meet or
exceed the requirements of the general
permit regulation (§ 22.210), except
where not practicable.
(5) If compensatory mitigation is
required, the applicant has proposed
either to implement compensatory
mitigation measures that comply with
the standards in § 22.220 or secure
required eagle credits from a Serviceapproved conservation bank or in-lieu
fee program. Compensatory mitigation
must meet or exceed the requirements of
the general permit regulation (§ 22.210),
except when the Service’s evaluation of
site-specific data indicates a lower
mitigation rate is appropriate.
(6) The applicant has proposed
monitoring plans that are sufficient to
determine the effects on eagle(s) of the
proposed activity.
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(7) The proposed reporting is
sufficient for the Service to determine
the effects on eagle(s).
(8) Any additional factors that may be
relevant to our decision whether to
issue the permit, including, but not
limited to, the cultural significance of a
local eagle population and whether
issuance of a permit would preclude the
Service from authorizing take necessary
to protect an interest of higher priority.
The Service will prioritize safety
emergencies, Native American Tribal
religious use, and public health and
safety.
(e) Modifications to your permit. If the
permittee requests substantive
amendments (see § 13.11(d)(5) of this
subchapter) during the permit tenure,
the Service will charge an amendment
fee. The Service will charge an
amendment fee and an administration
fee for permittee-requested substantive
amendments that require new analysis,
such as modifications that result in reestimating take, re-evaluating
compensatory mitigation requirements,
or requiring additional environmental
review to comply with procedural
requirements under NEPA.
(f) Tenure. The tenure of each permit
will be designated on the face of the
permit. Specific permits may be valid
for a maximum of 30 years. Permit
tenure may be less, as restricted by the
provisions for specific activities set
forth in § 22.250, § 22.260, § 22.280, or
§ 22.300 or as appropriate to the
duration and nature of the proposed
activity, including mitigation
requirements.
§ 22.210
General permits.
(a) Purpose. General permits authorize
the take of bald eagles or golden eagles
for other interests that meet the
eligibility requirements for general
permits set forth in § 22.250, § 22.260,
§ 22.280, or § 22.300.
(b) Eligibility. To qualify for a general
permit, you must be conducting an
activity identified in § 22.250, § 22.260,
§ 22.280, or § 22.300 and meet any
additional eligibility requirements
identified in the relevant section.
(1) Permits are issued to the
individual or entity conducting the
activity, such as the owner or manager
of the entity conducting the activity.
The applicant is responsible for
compliance with the permit and must
have the authority to implement the
required permit conditions.
(2) Contractors or consultants may
assist in completing applications or
conducting work as a subpermittee but
may not be a permit holder.
(3) Applicants may not break a project
into parts to meet general permit
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eligibility criteria when the entire
project would not be eligible.
(4) Applicants may not combine
projects if the activities are not readily
identifiable as being part of the same
project. If you want to obtain a
consolidated permit for multiple
activities, you must apply for a specific
permit.
(5) General permits are issued to a
single permit holder. If multiple entities
operate a joint project and want to
obtain joint authorization, the
application must designate one entity as
the permit holder and that entity must
accept the legal liability for the other
entities. The other entities must grant
sufficient authority to the permit holder
to carry out any activities required
under the permit.
(6) The Service may notify you in
writing that you must apply for a
specific permit if the Service finds that
the project does not comply with the
requirements for a general permit.
(c) How to apply. (1) Register with the
Service by submitting the appropriate
application form specified in
§ 22.250(a), § 22.260(a), § 22.280(a), or
§ 22.300(a) to Headquarters. You can
find the current contact information for
Migratory Birds in § 2.1 of subchapter A
of this chapter.
(2) Your application must include:
(i) A description of the activity that
will cause the take of bald eagles or
golden eagles, including the location,
and seasonality.
(A) If applying under § 22.250 for
wind energy projects, include the
number of turbines, rotor diameter, hub
height, location coordinates of each
turbine, and the datum of these
coordinates.
(B) If applying under § 22.260 for
power lines, include the State and
county(ies) of coverage and total miles
of transmission and distribution lines.
To the extent known, include the
number of miles or number of poles in
eagle-risk areas that are not avian-safe.
(C) If applying under § 22.280 or
§ 22.300, include the location of known
nests and nest status (i.e., in-use or
alternate).
(ii) Justification of why there is no
practicable alternative to take that
would protect the interest to be served.
(iii) Description of eagle activity and
eagle use in the project area.
(iv) Certification that the activity
involving the take of eagles authorized
by the general permit complies with all
other applicable Federal, State, Tribal,
and local laws. This includes certifying
that the activity for which take is to be
authorized by the general permit either
does not affect a property that is listed,
or is eligible for listing, in the National
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Register of Historic Places as maintained
by the Secretary of the Interior; or that
the applicant has obtained, and is in
compliance with, a written agreement
with the relevant State Historic
Preservation Officer or Tribal Historic
Preservation Officer that outlines all
measures the applicant will undertake
to mitigate or prevent adverse effects to
the historic property.
(v) Payment of required application
and administration fees (see
§ 13.11(d)(4) of this subchapter).
(vi) A certification that the applicant
agrees to acquire eagle credits, if
required, from a Service-approved
conservation bank or in-lieu fee program
within 90 days of the effective date of
the permit.
(d) Issuance criteria. Upon an
applicant registering by submitting an
application under paragraph (c) of this
section, the Service will automatically
issue a general permit to authorize the
take requested in the application. In
registering, you must certify that you
meet the general criteria of § 13.21 of
this subchapter and the following
issuance criteria:
(1) You are conducting an activity that
qualifies for a general permit.
(2) The take:
(i) Is necessary to protect a legitimate
interest in a particular locality;
(ii) Results from, but is not the
purpose of, the activity; and
(iii) Cannot practicably be avoided.
(3) The activity is consistent with the
requirements applicable to that activity
as specified in § 22.250, § 22.260,
§ 22.280, or § 22.300.
(4) You will implement the general
permit conditions applicable to your
activity, including required avoidance,
minimization, monitoring, and reporting
requirements.
(5) You will obtain any required eagle
credits from a Service-approved
conservation bank or in-lieu fee program
within 90 days of the effective date of
your permit.
(e) Program continuation. The Service
will regularly evaluate whether the take
of bald eagles and golden eagles under
general permits remains compatible
with the preservation of eagles. If the
Service finds, through analysis of the
best available information, that the
general permit program is not
compatible with the preservation of bald
eagles or golden eagles, the Service may
suspend issuing general permits in all or
in part after publishing notification in
the Federal Register. The Service may
reinstate issuance of general permits
after publishing another notification in
the Federal Register or by promulgating
additional rulemaking. If the Service
suspends general permitting, take
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currently authorized under a general
permit remains authorized until
expiration of that general permit, unless
you are notified otherwise.
(f) Tenure. The tenure of each permit
will be designated on the face of the
permit. General permits have a
maximum tenure of 5 years. Permit
tenure may be less, as restricted by the
applicable provisions in § 22.250,
§ 22.260, § 22.280, or § 22.300.
§ 22.215
Conditions of permits.
(a) Anyone conducting activities
under a specific permit (§ 22.200) or
general permit (§ 22.210) is subject to
the conditions set forth in this section.
You must also comply with the relevant
conditions set forth in subpart D of part
13 of this subchapter and the conditions
of your general or specific permit.
(1) Your permit will specify the type
of take authorized (e.g., incidental take,
disturbance, nest take) and may specify
the amount, location, or other
restrictions on the take authorized. You
are not authorized for any take not
specified on the face of your permit.
(2) Your permit will require
implementation of avoidance,
minimization, monitoring, and adaptive
management measures consistent with
the relevant regulations in this subpart
E. This may include requirements to:
(i) Modify the seasonality, frequency,
timing, duration, or other aspects of
your activity.
(ii) Implement measures to avoid and
minimize the take or effects of take on
eagles.
(iii) Monitor to determine the effects
of the activity on eagles according to
Service-approved protocols.
(iv) Implement an adaptive
management plan.
(3) Your permits will specify
requirements for reporting and
disposing of any discovered eagle
remains or injured eagles. Requirements
may include:
(i) Training onsite personnel and
requiring personnel to scan for
discovered eagle remains or injured
eagles;
(ii) Collecting information on
discovered eagle remains or injured
eagles, including species, condition,
discovery date, location, and other
information relevant to eagle
identification and determining the cause
of death or injury;
(iii) Reporting discovered eagle
remains or injured eagles, including
immediate notification and annual
reporting; and
(iv) Disposition of any discovered
eagle remains or injured eagles in
accordance with Service instructions,
which may include shipping eagles to
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the National Eagle Repository or other
designated facility.
(4) You must comply with all Service
reporting requirements. You must
annually report incidental take and
disturbance take using Form 3–202–15.
You must report nest take using Form
3–202–16. You must submit accurate
reports within the required timeline.
(5) You must comply with all
compensatory mitigation requirements
in accordance with § 22.220, including
any additional requirements contained
in § 22.250, § 22.260, § 22.280, or
§ 22.300.
(6) You must keep records of all
activities conducted under this permit,
including those of subpermittees carried
out under the authority of this permit
(see § 13.46 of this subchapter). You
must provide records to the Service
upon request.
(7) By accepting this permit, you are
authorizing the Service to:
(i) Publish the following information
in a public list of permittees: permittee
name, permit type, county and State of
activity, and effective date range.
(ii) Inspect the location and records
relating to the activity at the location
where those records are kept. Any
inspections will occur during regular
business hours (see § 13.21(e) of this
subchapter).
(iii) Provide access to Service staff or
contractors as part of participation in
the Service’s program-wide monitoring.
The Service will provide reasonable
notice for requests to access sites and
negotiate with the permittee about
practicable and appropriate access
conditions to protect human health and
safety and comply with any physical,
logistical, or legal constraints.
(8) You are responsible for ensuring
that the activity for which take is
authorized complies with all applicable
Federal, Tribal, State, and local laws,
regulations, and permits. You must
comply with all label instructions for
handling controlled substances and
chemicals, including pesticides.
(9) Permits are issued to the entity or
individual conducting the action.
(i) The Principal Officer is the chief
operating officer responsible for the
permit application and any permitted
activities. The Principal Officer is
responsible for compliance with all
conditions of authorization, including
the conditions listed here and any
permit conditions. The Principal Officer
must have the authority to implement
all conditions and is legally liable for
any subpermittee conducting activities
under the permit.
(ii) The authority of this authorization
may be exercised by subpermittees. A
subpermittee is any person who is
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employed by the authorized entity to
conduct the activities specified or any
person designated as a subpermittee in
writing by the Principal Officer.
Subpermittee-designation letters must
identify who can conduct what
activities and list any restrictions on the
dates, locations, or types of activities the
subpermittee may conduct.
(iii) The Principal Officer is
responsible for any subpermittee who is
conducting authorized activities.
Subpermittees must have the conditions
of authorization and, if applicable, a
copy of the permit readily available.
Subpermittees who are not employees
must also have a subpermitteedesignation letter.
(b) The Service may amend, suspend,
or revoke a permit issued under this
subpart if new information indicates
that revised permit conditions are
necessary, or that suspension or
revocation is necessary, to safeguard
local or regional eagle populations. This
provision is in addition to the general
criteria for amendment, suspension, and
revocation of Federal permits set forth
in §§ 13.23, 13.27, and 13.28 of this
subchapter.
(c) Notwithstanding the provisions of
§ 13.26 of this subchapter, you remain
responsible for all outstanding
monitoring requirements and mitigation
measures required under the terms of
the permit for take that occurs prior to
cancellation, expiration, suspension, or
revocation of the permit.
§ 22.220
Compensatory mitigation.
(a) Your permit conditions may
include a requirement to compensate for
the take of eagles.
(1) Any permit authorizing take that
would exceed the applicable EMU take
limit will require compensatory
mitigation, except in circumstances
where the action is considered in the
best interest of an eagle. Compensatory
mitigation for this purpose must ensure
the preservation of the affected eagle
species by mitigating an amount equal
to or greater than the authorized or
expected take. Compensatory mitigation
must either reduce another ongoing
form of mortality or increase the eagle
population of the affected species.
Compensatory mitigation for golden
eagles must be performed at a 1.2:1
(mitigation: take) ratio.
(2) A permit may require
compensatory mitigation when the
Service determines, according to the
best available information, that the take
authorized by the permitted activity is
not consistent with maintaining the
persistence of the local area population
of an eagle species.
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9961
(b) All required compensatory
mitigation actions must:
(1) Be contingent upon application of
avoidance and minimization measures
to reduce the take to the maximum
degree practicable relative to the
magnitude of the project’s impacts on
eagles.
(2) Be sited within:
(i) The same EMU where the
permitted take will occur; or
(ii) Another EMU if the Service has
reliable data showing that the
population affected by the take includes
individuals that are reasonably likely to
use that EMU during part of their
seasonal migration.
(3) If required by the Service, be sited
within a specified local area population.
(4) Use the best available science in
formulating, crediting, and monitoring
the long-term effectiveness of mitigation
measures.
(5) Be additional to and improve upon
the baseline conditions for the affected
eagle species in a manner that is
demonstrably new and would not have
occurred without the compensatory
mitigation.
(6) Be durable and, at a minimum,
maintain its intended purpose for as
long as required by the mitigation
conditions in the permit.
(7) Include mechanisms to account for
and address uncertainty and risk of
failure of a compensatory mitigation
measure.
(8) Include financial assurances that
the required compensatory mitigation
measures will be implemented in full.
(c) Compensatory mitigation must be
approved by the Service and may
include conservation banks, in-lieu fee
programs, or permittee-responsible
mitigation as mitigation providers.
(1) General permittees meet this
requirement by obtaining required
credits from a Service-approved, thirdparty mitigation provider. Specific
permittees can meet this requirement by
obtaining required credits from a
Service-approved, third-party mitigation
provider or meeting the requirements to
be a permittee-responsible mitigation
provider as described in paragraph (c)(2)
of this section. Third-party mitigation
providers (e.g., in-lieu fee programs and
conservation banks) obtain Service
approval by meeting the requirements to
be a mitigation provider as described in
paragraph (c)(2) of this section.
(2) To obtain approval as a mitigation
provider, potential providers must
submit a mitigation plan to the Service
that demonstrates how the standards set
forth in paragraph (b) of this section will
be met. At a minimum, this must
include a description of the mitigation,
the benefit to eagles, the locations where
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projects will be implemented, the EMU
and local area population affected, the
number of credits provided, and an
explanation of the rationale for the
number of eagle credits provided. The
Service must approve the mitigation
plan prior to implementation.
§ 22.250 Permits for incidental take of
eagles by wind energy projects.
(a) Purpose. The regulations in this
section authorize the incidental killing
or injury of bald eagles and golden
eagles associated with the operation of
wind energy projects. Apply using Form
3–200–71.
(b) Definition. The following term
used in this section has the meaning set
forth in this paragraph (b):
Existing project. Infrastructure that
was operational prior to May 13, 2024,
as well as infrastructure that was
sufficiently far along in the planning
process on that date that complying
with new requirements would be
impracticable, including if an
irreversible or irretrievable commitment
of resources has been made (e.g., site
preparation was already underway or
infrastructure was partially
constructed).
(c) Eligibility for a general permit. To
qualify for a general permit, you must
meet the requirements of § 22.210, be
located in the contiguous 48 States, not
have discovered four or more eagles of
one species in the previous 5 years per
paragraph (d)(3) of this section, and:
(1) Be a project applying for a general
permit for the first time, and all turbines
associated with the project are:
(i) At least 2 miles from a golden eagle
nest and at least 660 feet from a bald
eagle nest; and
(ii) Located in areas characterized by
seasonal relative abundance values that
are less than the relative abundance
values for the date range for each
species in tables 1 and 2:
TABLE 1 TO PARAGRAPH (c)(1)(ii)—RELATIVE ABUNDANCE VALUE THRESHOLDS FOR BALD EAGLES THROUGHOUT THE
YEAR
Bald Eagle
relative
abundance
Date range
1.
2.
3.
4.
February 15–May 23 .......................................................................................................................................................................
May 24–July 19 ...............................................................................................................................................................................
July 20–December 20 .....................................................................................................................................................................
December 21–February 14 .............................................................................................................................................................
0.821
0.686
0.705
1.357
TABLE 2 TO PARAGRAPH (c)(1)(ii)—RELATIVE ABUNDANCE VALUE THRESHOLDS FOR GOLDEN EAGLES THROUGHOUT THE
YEAR
Golden Eagle
relative
abundance
Date range
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1.
2.
3.
4.
February 8–June 6 ..........................................................................................................................................................................
June 7–August 30 ...........................................................................................................................................................................
August 31–December 6 ...................................................................................................................................................................
December 7–February 7 .................................................................................................................................................................
(2) Be a project currently authorized
under a general permit that:
(i) Has discovered fewer than four
eagles (either eagle remains or injured
eagles) of any one species during the
previous general permit tenure;
(ii) Had no lapse in general-permit
coverage; and
(iii) Ensures that any turbines not
authorized on the previous general
permit meet the issuance criteria in
paragraph (c)(1) of this section.
(3) Be an existing project that has
received a letter of authorization from
the Service (see § 22.200(b)(7)).
(d) Discovered eagle provisions for
general permits. You must implement
procedures to discover eagle remains
and injured eagles in accordance with
§ 22.215(a)(3) and as required by your
permit conditions. In following those
protocols:
(1) You must include in your annual
report the discovery of any eagle
remains or injured eagles.
(2) If you discover eagle remains or
injured eagles of three eagles of any one
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species during the tenure of a general
permit, you must notify the Service in
writing within 2 weeks of discovering
the take of a third eagle and implement
adaptive management measures. When
notifying the Service, you must include
the reporting data required by your
permit conditions, your adaptive
management plan, and a description
and justification of the adaptive
management approaches you will
implement for the remaining duration of
your general permit.
(3) If you discover eagle remains or
injured eagles of four eagles of any one
species during the tenure of a general
permit, you must notify the Service in
writing within 2 weeks of discovering
the take of the fourth eagle. When
notifying the Service, you must include
the reporting data required by your
permit conditions, your adaptive
management plan, and a description
and justification of the adaptive
management approaches you will
implement for the remaining duration of
your general permit term. The project
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0.081
0.065
0.091
0.091
will remain authorized to incidentally
take eagles through the term of the
existing general permit but will not be
eligible for future general permits. You
may instead apply for a specific permit
for incidental take at that project. You
may request reconsideration of generalpermit eligibility by following the
review procedures set forth at § 13.29 of
this subchapter, including providing the
information required in § 13.29(b)(3).
(4) If the Service conducts monitoring
at a wind project, eagle remains or
injured eagles discovered by the
Service, or Service contractor, are not
attributed to the project for the purposes
of this paragraph (d), unless the Service
determines the eagles were also
discovered, or were likely to have been
discovered, by required monitoring
efforts at the project.
(e) Eligibility for a wind energy
specific permit. To qualify for a specific
permit, you must meet the requirements
of § 22.200. In determining whether to
issue a permit, the Service will review
the application materials provided,
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including the eagle impacts assessment.
The Service will determine, using the
best available data, the expected take of
eagles by the proposed activity.
(f) Wind energy permit conditions.
The following conditions apply to all
general and specific permits. Specific
permits may include additional projectspecific permit conditions.
(1) Develop and implement an
adaptive management plan. An adaptive
management plan applies the best
available science and monitoring to
refine project operations and practices.
Plans identify criteria for
implementation of the mitigation
hierarchy, including avoidance,
minimization, and compensation to
remain consistent with permit
conditions and the preservation of
eagles.
(2) Remove and avoid creating
anthropogenic features that increase the
risk of eagle take by attracting eagles to
the project site or encouraging foraging,
roosting, or nesting behaviors.
(3) Minimize collision and
electrocution risks, including collisions
with turbines, vehicles, towers, and
power lines.
(4) Comply with all relevant
regulations and permit conditions in
part 21 of this subchapter.
(5) Submit required reports to the
Service by the applicable deadline.
(6) Pay the required application and
administration fees (see § 13.11(d)(4) of
this subchapter).
(7) Implement required compensatory
mitigation. You must keep records to
document compliance with this
requirement and provide them to the
Service with your annual report.
(i) For wind energy specific permits,
you must submit a plan to the Service
in accordance with § 22.200(c) and
implement the compensatory-mitigation
requirements included on the face of
your permit.
(ii) For wind energy general permits,
you must obtain eagle credits from a
Service-approved conservation bank or
in-lieu fee program based on the
hazardous volume of the project (in
cubic kilometers). The hazardous
volume of a project is calculated as the
number of turbines multiplied by
0.200p(d/2)∧2 where d is the diameter of
the blades in kilometers. You must
obtain eagle credits at the following
rates: Atlantic/Mississippi EMUs: 6.02
eagles/km3, Central EMU: 7.46 eagles/
km3, and Pacific EMU: 11.12 eagles/
km3.
(g) Tenure of permits. General permits
are valid for 5 years from the date of
registration. Specific permits may be
valid for up to 30 years.
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§ 22.260 Permits for incidental take of
eagles by power lines.
(a) Purpose. The regulations in this
section authorize the incidental killing
or injury of bald eagles and golden
eagles associated with power line
activities. Apply using Form 3–200–71.
(b) Definitions. The following terms
used in this section have the meanings
set forth in this paragraph (b):
Avian-safe. A power-pole
configuration designed to minimize
avian electrocution risk by providing
sufficient separation between phases
and between phases and grounds to
accommodate the wrist-to-wrist or headto-foot distance of the bird. For eagles,
this is 150 centimeters of horizontal
separation and 100 centimeters of
vertical separation. If sufficient
separation cannot be provided, exposed
parts that conduct electricity must be
covered to reduce electrocution risk. If
covers are used, they must be
maintained in good condition. For
conversions from an above-ground line
to a buried line, the buried portion is
considered ‘‘avian-safe.’’ For purposes
of the regulations in this section,
‘‘avian-safe’’ means safe for eagles.
Collision response strategy. A plan
that describes the process the permittee
will follow to identify whether a
collision-caused injury or mortality has
occurred, to evaluate factors that
contributed to the collision, and to
implement risk-reduction measures
commensurate with the collision risk.
Proactive retrofit strategy. A plan to
convert existing infrastructure to aviansafe infrastructure within a set timeline.
The strategy must identify a baseline of
poles to be proactively retrofit. The
existing-infrastructure baseline must
include all poles that are not avian-safe
for eagles located in areas identified as
high risk to eagles and may also include
other poles in the service area.
Reactive retrofit strategy. A plan to
respond to incidents where eagles are
electrocuted or killed. The reactive
retrofit strategy must include
information on how eagle electrocutions
are detected and identified. Determining
which poles to retrofit must be based on
the risk to eagles and not on other
factors (e.g., convenience or cost). The
pole that caused the electrocution must
be retrofitted unless the pole is already
avian-safe. A total of 13 poles or a halfmile segment must be retrofitted,
whichever is less, prioritizing the
highest risk poles closest to the
electrocution event.
Shooting response strategy. A plan
that describes the process the permittee
will follow when eagles are found killed
or injured near power-line infrastructure
to identify if shooting is suspected, to
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9963
communicate with law enforcement,
and to identify and implement
appropriate shooting reduction
measures.
(c) Eligibility for a general permit for
incidental take. To qualify for a general
permit, you must meet the requirements
of § 22.210.
(d) General permit conditions for
power lines. Project permittees must:
(1) Develop a reactive retrofit strategy
and implement that strategy following
each discovery of an electrocuted eagle.
The investigation, documentation, and
retrofit design selection must be
completed within 90 days of the
incident. The retrofit must be
implemented within 1 year of the
incident and remain effective for 30
years.
(2) Implement a proactive retrofit
strategy to convert all existinginfrastructure-baseline poles to aviansafe. Retrofits must remain effective for
30 years.
(i) Investor-owned utilities must
retrofit all existing-infrastructurebaseline poles within 50 years. Ten
percent of baseline poles must be
converted to avian-safe during each
permit tenure unless extenuating
circumstances apply.
(ii) Non-investor-owned utilities must
retrofit all existing-infrastructurebaseline poles within 75 years. Seven
percent of baseline poles must be
converted to avian-safe during each
permit tenure unless extenuating
circumstances apply.
(3) Implement an eagle collision
response strategy. Within 90 days of a
collision, you must complete an
investigation where the collision
occurred by documenting the factors
contributing to the collision and
identifying appropriate risk-reduction
measures. You must implement selected
risk-reduction measures at the location
of the collision within 1 year of the
incident.
(4) Implement an eagle shooting
response strategy. The strategy must
include a protocol for immediately
contacting the Office of Law
Enforcement (in no case more than 72
hours from discovery) when finding
eagle remains or an injured eagle near
power line infrastructure in
circumstances that suggest the eagle
may have been shot. If multiple
shooting events occur in the service area
during the permit tenure, the strategy
should describe and provide for the
implementation of reasonable shootingreduction measures.
(5) Train personnel to scan for eagle
remains when onsite and implement
internal reporting and recordkeeping
procedures for discovered eagles.
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(6) Ensure that all new construction
and rebuild or replacement of poles in
areas of high risk for eagles is avian-safe
unless this requirement would unduly
impact human health and safety, require
overly burdensome engineering, or have
significant adverse effects on biological,
cultural, or historical resources.
(7) For new construction and rebuild,
reconstruction, or replacement projects,
incorporate information on eagles into
siting and design considerations.
Minimize eagle risk by siting away from
eagle-use areas (e.g., nests and winter
roosts), accounting for the risk to and
population status of the species, unless
this requirement would unduly impact
human health and safety; require overly
burdensome engineering; or have
significant adverse effects on biological,
cultural, or historical resources.
(8) Comply with all relevant
regulations and permit conditions of
part 21 of this subchapter.
(9) Submit required reports to the
Service using Form 3–202–15.
(10) Pay the required application and
administration fee as set forth in
§ 13.11(d)(4) of this subchapter.
(e) Specific permit for incidental
take—(1) Eligibility. Any entity
conducting power line activities that
meet the requirements of § 22.200 may
apply for a specific permit.
(2) Conditions. You must comply with
the conditions required in § 22.200.
Your permit conditions will include the
relevant general-permit conditions from
paragraph (d) of this section.
Compensatory mitigation may be
required when appropriate, including if
general permit conditions cannot be
met.
(f) Tenure of permits. Power line
general permits are valid for 5 years.
Specific permits may be valid for up to
30 years.
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§ 22.280
eagles.
Permits for disturbance take of
(a) Purpose. The regulations in this
section authorize the take of bald eagles
or golden eagles by disturbance, as
defined in § 22.6. Apply using Form 3–
200–91. Permits to authorize
disturbance associated with hazing
eagles or eagle nest take are not
authorized under this section. A permit
is not required when an activity that
may ordinarily disturb eagles is ongoing
at the time an eagle pair initiates nesting
because the nesting eagles are presumed
to tolerate the activity.
(b) Eligibility for a general permit for
disturbance. To qualify for a general
permit, you must meet the requirements
of § 22.210, and your activities must
comply with the provisions set forth in
paragraphs (b)(1) through (9) of this
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21:12 Feb 09, 2024
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section. If permanent loss of a territory
may occur, a specific permit is
recommended because general permits
for disturbance do not authorize the
permanent loss of a territory. General
permits are not available if the nest is
located in Indian country (18 U.S.C.
1151), unless the Tribe is the applicant.
The following activities are eligible for
a general permit:
(1) Building construction and
maintenance within 660 feet of a bald
eagle nest.
(2) Linear infrastructure construction
and maintenance (e.g., roads, rail, trails,
power lines, and other utilities) within
660 feet of a bald eagle nest.
(3) Alteration of shorelines and water
bodies (e.g., shorelines, wetlands, docks,
moorings, marinas, and water
impoundment) within 660 feet of a bald
eagle nest.
(4) Alteration of vegetation (e.g.,
mowing, timber operations, and forestry
practices) within 660 feet of a bald eagle
nest.
(5) Motorized recreation (e.g.,
snowmobiles, motorized watercraft, etc.)
within 330 feet of an in-use bald eagle
nest.
(6) Nonmotorized recreation (e.g.,
hiking, camping, fishing, hunting,
canoeing, etc.) within 330 feet of an inuse bald eagle nest.
(7) Aircraft operation (e.g., helicopters
and fixed-wing aircraft) within 1,000
feet of an in-use bald eagle nest.
(8) Prescribed burn operations within
660 feet of a bald eagle nest.
(9) Loud, intermittent noises (e.g.,
blasting) within one-half-mile of an inuse bald eagle nest.
(c) Eligibility for a specific permit for
disturbance. To qualify for a specific
permit, you must meet the requirements
of § 22.200. Specific permits are for
disturbance of a golden eagle nest,
disturbance of a bald eagle nest by an
activity not specified in paragraph (b) of
this section, or disturbance of eagles
caused by physical or functional
elimination of all foraging area within a
territory.
(d) Disturbance permit conditions. (1)
To the maximum degree practicable,
implement measures to avoid and
minimize nest disturbance, including
disturbance due to noise from human
activities, visibility of human activities,
proximity of activities to the nest,
habitat alteration, and any indirect
stressors.
(2) Avoid activities that may
negatively affect the nesting substrate,
including the survival of the nest tree.
(3) Monitor in-use nests sufficiently to
determine whether nestlings have
fledged from the nest. Include this
information in your annual report.
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(e) Reporting. You must submit an
annual report using Form 3–202–15.
The annual report is due on the date
specified on your permit or prior to
requesting renewal of your permit,
whichever is first.
(f) Tenure of permits. General permits
for disturbance issued under the
regulations in this section are valid for
a maximum of 1 year. The tenure of
specific permits for disturbance is set
forth on the face of the permit and may
not exceed 5 years.
§ 22.300
Permits for take of eagle nests.
(a) Purpose. This section authorizes
the take of a bald eagle nest or a golden
eagle nest, including relocation,
removal, and otherwise temporarily or
permanently preventing eagles from
using the nest structure for breeding,
when there is no practicable alternative
that would protect the interest to be
served. Apply using Form 3–200–72.
(b) Definitions. The following terms
used in this section have the meanings
set forth in this paragraph (b):
Nest take for emergency. Take of an
in-use or alternate eagle nest when
necessary to alleviate an existing safety
emergency for humans or eagles or to
prevent a rapidly developing situation
that is likely to result in a safety
emergency for humans or eagles.
Nest take for health and safety. Take
of an eagle nest when the removal is
necessary to ensure public health and
safety. Nest take for health and safety is
limited to in-use nests prior to egg
laying or alternate nests.
Nest take for human-engineered
structure. Take of an eagle nest built on
a human-engineered structure that
creates, or is likely to create, a
functional hazard that renders the
structure inoperable for its intended
use. Take is limited to in-use nests prior
to egg-laying or alternate nests.
Nest take for species protection. Take
of an eagle nest when nest removal is
necessary to protect a species federally
protected under the Endangered Species
Act of 1973, as amended (16 U.S.C.
1531–1544) and included on the List of
Endangered and Threatened Wildlife (at
§ 17.11 of this subchapter). Take is
limited to in-use nests prior to egg
laying or alternate nests.
Other purposes. Take of an alternate
eagle nest, provided the take is
necessary to protect an interest in a
particular locality and the activity
necessitating the take or the mitigation
for the take will, with reasonable
certainty, provide a net benefit to eagles.
(c) Eligibility for a general permit for
nest take. To qualify for a general
permit, you must meet the requirements
of § 22.210.
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(1) General permits are available for
bald eagle nest take for emergency, nest
take for health and safety, or nest take
for a human-engineered structure, or, if
located in Alaska, other purposes.
(2) General permits are not available
for take of golden eagle nests. General
permits are not available for bald eagle
nests if removal may result in the
complete loss of a territory.
(3) General permits are not available
if the nest is located in Indian country
(18 U.S.C. 1151), unless the Tribe is the
applicant.
(d) Eligibility for a specific permit for
nest take. To qualify for a specific
permit, you must meet the requirements
of § 22.200. Specific permits are
required for take of a golden eagle nest
for any purpose, nest take for species
protection, and, except in Alaska, nest
take for other purposes.
(e) Permits for species protection. If
you are applying for a nest-take permit
for species protection, you must:
(1) Be a Federal, State, or Tribal
agency responsible for implementing
actions for the protection of the species
of concern.
(2) Include documentation that:
(i) Describes relevant management
efforts to protect the species of concern.
(ii) Identifies and describes how the
nesting eagles are a limiting factor to
recovery of the species using the best
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21:12 Feb 09, 2024
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available scientific information and
data.
(iii) Explains how take of eagle nests
is likely to have a positive effect on
recovery for the species of concern.
(f) Permit conditions for nest take.
Permit conditions may include
requirements to:
(1) Adjust the timing of your activity
to minimize the effects of nest take on
eagles.
(2) Place an obstruction in the nest or
nest substrate.
(3) Minimize or deter renesting
attempts that would cause the same
emergency, safety, or functional hazard.
(4) Relocate the nest or provide
suitable nesting substrate within the
same territory.
(5) Remove chicks or eggs from an inuse nest for immediate transport to a
foster nest, rehabilitation facility, or as
otherwise directed by the Service.
(6) If nestlings or eggs are relocated
with a nest or to a foster nest, monitor
the nest to ensure adults are tending to
nestlings or eggs.
(7) Monitor the area near the nest
removal for one or more seasons to
determine the effect on eagles.
(8) Submit an annual report using
Form 3–202–16.
(g) Tenure of permits. General permits
issued under this section are valid until
the start of the next breeding season, not
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9965
to exceed 1 year. The tenure of specific
permits is set forth on the face of the
permit and may not exceed 5 years.
§ 22.75
[Redesignated as § 22.235]
14. Redesignate § 22.75 as § 22.325
and transfer to subpart E.
■ 15. Amend newly designated § 22.325
by:
■ a. Revising the section heading; and
■ b. In the introductory text, removing
the three sentences that follow the first
sentence.
The revision reads as follows:
■
§ 22.325 Permits for golden eagle nest
take for resource recovery operations.
*
*
§ 22.90
*
*
*
[Redesignated as § 22.400]
16. Redesignate § 22.90 as § 22.400
and transfer to subpart E.
■
§ 22.400
[Amended]
17. Amend newly designated § 22.400
in paragraphs (a) and (b) by removing
the words ‘‘the effective date of 50 CFR
22.80’’ and adding in their place the
words ‘‘November 10, 2009’’.
■
Shannon A. Estenoz,
Assistant Secretary for Fish and Wildlife and
Parks.
[FR Doc. 2024–02182 Filed 2–8–24; 8:45 am]
BILLING CODE 4333–15–P
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Agencies
[Federal Register Volume 89, Number 29 (Monday, February 12, 2024)]
[Rules and Regulations]
[Pages 9920-9965]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2024-02182]
[[Page 9919]]
Vol. 89
Monday,
No. 29
February 12, 2024
Part II
Department of the Interior
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Fish and Wildlife Service
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50 CFR Parts 13 and 22
Permits for Incidental Take of Eagles and Eagle Nests; Final Rule
Federal Register / Vol. 89 , No. 29 / Monday, February 12, 2024 /
Rules and Regulations
[[Page 9920]]
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DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Parts 13 and 22
[Docket No. FWS-HQ-MB-2020-0023; FF09M30000-234-FXMB12320900000]
RIN 1018-BE70
Permits for Incidental Take of Eagles and Eagle Nests
AGENCY: Fish and Wildlife Service, Interior.
ACTION: Final rule.
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SUMMARY: We, the U.S. Fish and Wildlife Service, are revising the
regulations for the issuance of permits for eagle incidental take and
eagle nest take. The purpose of these revisions is to increase the
efficiency and effectiveness of permitting, improve clarity for the
regulated community, and increase the conservation benefit for eagles.
In addition to continuing to authorize specific permits, we created
general permits for certain activities under prescribed conditions,
including general permit options for qualifying wind-energy generation
projects, power line infrastructure, activities that may disturb
breeding bald eagles, and bald eagle nest take. We also made
improvements to the specific permit requirements and process. We also
revised permit fees and clarified definitions.
DATES: Effective April 12, 2024.
Information Collection Requirements: If you wish to comment on the
information collection requirements in this rule, please note that the
Office of Management and Budget (OMB) is required to make a decision
concerning the collection of information contained in this rule between
30 and 60 days after the date of publication of this rule in the
Federal Register. Therefore, comments should be submitted to OMB by
March 13, 2024.
ADDRESSES:
Document availability: The finding of no significant impact, final
environmental assessment, and supplementary information used in
development of this rule, including a list of references cited,
technical appendices, and public comments received are available at
https://www.regulations.gov in Docket No. FWS-HQ-MB-2020-0023.
Documents and additional information can also be found at: https://www.fws.gov/regulations/eagle.
Information Collection Requirements: Written comments and
suggestions on the information collection requirements should be
submitted within 30 days of publication of this document to https://www.reginfo.gov/public/do/PRAMain. Find this particular information
collection by selecting ``Currently under Review--Open for Public
Comments'' or by using the search function. Please provide a copy of
your comments to the Service Information Collection Clearance Officer,
U.S. Fish and Wildlife Service, 5275 Leesburg Pike, MS: PRB (JAO/3W),
Falls Church, VA 22041-3803 (mail); or [email protected] (email).
Please reference OMB Control Number 1018-0167 in the subject line of
your comments.
FOR FURTHER INFORMATION CONTACT: Jerome Ford, Assistant Director--
Migratory Birds Program, U.S. Fish and Wildlife Service, telephone:
(703) 358-2606, email: [email protected]. Individuals in the United
States who are deaf, deafblind, hard of hearing, or have a speech
disability may dial 711 (TTY, TDD, or TeleBraille) to access
telecommunications relay services. Individuals outside the United
States should use the relay services offered within their country to
make international calls to the point-of-contact in the United States.
SUPPLEMENTARY INFORMATION:
Background
The U.S. Fish and Wildlife Service (Service) is the Federal agency
delegated with the primary responsibility for managing bald eagles
(Haliaeetus leucocephalus) and golden eagles (Aquila chrysaetos) under
the Bald and Golden Eagle Protection Act 16 U.S.C. 668-668d;
[hereinafter the ``Eagle Act'']). The Eagle Act prohibits the take,
possession, and transportation of bald eagles and golden eagles except
pursuant to Federal regulations. The Eagle Act authorizes the Secretary
of the Interior to issue regulations to permit the ``taking'' of eagles
for various purposes, including when ``necessary . . . for the
protection of other interests in any particular locality,'' provided
the taking is compatible with the preservation of eagles (16 U.S.C.
668a). Regulations pertaining to eagle permits are set forth in title
50 of the Code of Federal Regulations (CFR) at 50 CFR part 22. These
regulations authorize the take of eagles by an activity: They do not
purport to nor can they authorize the underlying activity itself.
In 2009, subsequent to the delisting of the bald eagle from the
List of Endangered and Threatened Wildlife at 50 CFR 17.11, the Service
promulgated regulations (74 FR 46836, Sept. 11, 2009 [hereinafter the
``2009 Eagle Rule'']) at 50 CFR part 22 that established two new permit
types for the incidental take of eagles and eagle nests. Incidental
take means foreseeable take that results from, but is not the purpose
of, an activity. These regulations were revised in 2016 (81 FR 91494,
December 16, 2016 [hereinafter the ``2016 Eagle Rule'']) to extend
tenure, update the Service's Eagle Management Unit (EMU) boundaries,
require preconstruction monitoring for wind-energy projects, and to
amend the preservation standard. The 2016 Eagle Rule was supported by a
programmatic environmental impact statement (PEIS), and the Service's
final decision was described in a record of decision, both of which are
available at https://www.regulations.gov in Docket No. FWS-R9-MB-2011-
0094.
On September 14, 2021, the Service published an advance notice of
proposed rulemaking (ANPR) to inform the public of changes the Service
is considering that expedite and simplify the permit process
authorizing incidental take of eagles (86 FR 51094). The ANPR also
advised the public that the Service may prepare a draft environmental
review pursuant to the National Environmental Policy Act of 1969, as
amended. In the ANPR, we invited input from Tribes, Federal agencies,
State agencies, nongovernmental organizations, and the general public
for any pertinent issues we should address, including alternatives to
our proposed approach for authorizing eagle incidental take. The public
comment period closed on October 29, 2021. The Service used these
comments to prepare a proposed rule and a draft environmental
assessment (DEA) which we released on September 30, 2022 (87 FR 59598).
The 60-day public comment period was extended to December 29, 2022 (87
FR 72957, November 28, 2022). The DEA and proposed rule are available
in Docket No. FWS-HQ-MB-2020-0023 (available at https://www.regulations.gov).
Comments and materials we received, as well as supporting
documentation we use in preparing the environmental analysis, are
available for public inspection. For more information on public
comments see the Response to Public Comments below. The Service also
announces the availability of the finding of no significant impact
(FONSI) for the Service's final environmental assessment (FEA). The
FONSI is the final step in the National Environmental Policy Act (NEPA)
process for this eagle rulemaking action, which includes revisions to
the regulations governing permits for incidental take of eagles and
take of eagle nests. The FONSI and FEA are available in Docket No. FWS-
HQ-
[[Page 9921]]
MB-2020-0023 (available at https://www.regulations.gov).
With this rulemaking, we do not change the 2016 preservation
standard or PEIS management objectives. The Eagle Act and existing
regulations require that any authorized take of eagles be ``compatible
with the preservation'' of bald and golden eagles (16 U.S.C. 668a).
Under existing regulations, the preservation standard is defined as
consistent with the goals of maintaining stable or increasing breeding
populations in all eagle management units and the persistence of local
populations throughout the geographic range of each species (50 CFR
22.6).
In 2009, the Service adopted different management criteria for bald
eagles and golden eagles because of the different population statuses
and growth rates of each species. We determined this approach is
necessary both to achieve the preservation standard and to avoid being
unnecessarily restrictive. We do not alter this approach with this
rulemaking. In this rulemaking, the Service uses the recently updated
population-size estimates and allowable take limits for bald eagles (87
FR 5493, February 1, 2022).
This Rulemaking
Overview
The Service creates a new subpart E within 50 CFR part 22 for eagle
permit regulations authorizing take that is necessary for the
protection of other interests in any particular locality (eagle take
for other interests). This new subpart includes revised provisions for
processing specific permits and creates general permits. General
permits authorize incidental take by activity type that occur
frequently enough for the Service to have developed a standardized
approach to permitting and ensure permitting is consistent with the
preservation standard. These regulations also restructure the existing
specific permit regulations. These regulations apply, regardless of
whether infrastructure is constructed before or after the final
regulations.
We amend these regulations to better align with the purpose and
need described in the 2016 PEIS. In the 2016 Eagle Rule, the Service
sought to:
(1) increase compliance by simplifying the permitting framework and
increasing certainty;
(2) allow for consistent and efficient administration of the
program by Service staff;
(3) regulate based on best available science and data; and
(4) enhance protection of eagles throughout their ranges by
increasing implementation of avoidance, minimization, and mitigation of
adverse impacts from human activities.
In this rulemaking, we create a new subpart E for regulations
governing the permitting of eagle take for other interests. We adopt
two regulations for administering permitting: specific permits (Sec.
22.200) and general permits (Sec. 22.210). We further specify
activity-specific eligibility criteria and permit requirements in four
sections based on activity and type of eagle take:
incidental take for permitting wind energy (Sec. 22.250),
incidental take for permitting power lines (Sec. 22.260),
disturbance take (Sec. 22.280), and
nest take (Sec. 22.300).
For clarity and consistency, we have also moved regulatory content
on permit conditions to a new section (Sec. 22.215) and content on
compensatory mitigation standards to a new section (Sec. 22.220). We
have created new definitions to define ``general permit'' and
``incidental take'' and included clarifying modifications to the
definitions of ``eagle management unit,'' ``eagle nest,'' and ``in-use
nest'' (Sec. 22.6). We have redesignated related regulations
pertaining to permit requirements for take of golden eagle nests (moved
from Sec. 22.75 to Sec. 22.325) and permits for bald eagle take
exempted under the Endangered Species Act (moved from Sec. 22.90 to
Sec. 22.400) to a new subpart E, with only the modification of a
nonsubstantive change to the section title for Sec. 22.325. Finally,
we have adopted administrative updates to 50 CFR part 13, General
Permit Procedures, to update the text regarding information-collection
requirements and the table of application fees. These changes to the
designated section numbers for previous regulations are as follows:
----------------------------------------------------------------------------------------------------------------
New sections in
Previous regulations in 50 CFR part 22 Regulatory subject matter 50 CFR part 22,
subpart E
----------------------------------------------------------------------------------------------------------------
Sec. Sec. 22.80 and 22.85.............................. Specific permits................. Sec. 22.200
General permits.................. Sec. 22.210
Sec. Sec. 22.80 and 22.85.............................. Permit conditions................ Sec. 22.215
Sec. 22.80.............................................. Compensatory mitigation.......... Sec. 22.220
Sec. 22.80.............................................. Wind energy project incidental Sec. 22.250
take.
Sec. 22.80.............................................. Power line incidental take....... Sec. 22.260
Sec. 22.80.............................................. Eagle disturbance take........... Sec. 22.280
Sec. 22.85.............................................. Eagle nest take.................. Sec. 22.300
Sec. 22.75.............................................. Golden eagle nest take for Sec. 22.325
resource recovery operations.
Sec. 22.90.............................................. Bald eagle take exempted under Sec. 22.400
the Endangered Species Act.
----------------------------------------------------------------------------------------------------------------
Specific Permits and General Permits for Eagle Take
Under these new and updated regulations, the Service will authorize
eagle take using general permits and specific permits. General permits
simplify and expedite the permitting process for activities that have
relatively consistent and low risk to eagles and well-established
avoidance, minimization, and compensatory mitigation measures. General-
permit applicants self-identify eligibility and register with the
Service. This includes providing required application information and
fees and certifying that they meet eligibility criteria and will
implement permit conditions and reporting requirements.
The Service will implement general permits for the following
activities: (1) certain categories of bald eagle nest take, (2) certain
activities that may cause bald eagle disturbance take, (3) eagle
incidental take associated with power line infrastructure, and (4)
eagle incidental take associated with certain wind energy projects.
These are described in more detail in the following sections. The
Service will audit general permits to ensure applicants are
appropriately interpreting and applying eligibility criteria and
complying with permit conditions. Audits will include reviewing
submitted application materials and reports. The Service will also
request and review any plans or strategies
[[Page 9922]]
required by permit conditions, like adaptive management plans.
The Service will continue to issue specific permits, which require
submission of application materials to the Service for review and
development of permit conditions. To maintain a review process adequate
to meet the preservation standard for eagles, the Service retains the
specific-permit approach for situations that have increased or
uncertain risks to eagles. The applicant is responsible for submitting
a qualifying application. The Service will determine, based on the
materials provided, whether the application meets regulatory
requirements. The Service is responsible for identifying and using the
best available information in making these determinations. If an
applicant is unable to meet Service data standards in applying, the
Service may waive these data standards provided: (1) the application
otherwise meets issuance criteria, (2) the Service has adequate
information to estimate take, and (3) the waiver will be consistent
with preservation of the eagle species. There is no process to petition
the Service for a waiver; rather, this process will be at the Service's
discretion and documented in the permit file. Specific permit
conditions must meet or exceed the requirements of general permits,
except when not practicable or when site-specific data warrants
customization.
If the best available information indicates that continuing
implementation of a general permit program is inconsistent with the
preservation of bald eagles or golden eagles, the Service may suspend
the general permit program temporarily or indefinitely. This suspension
may apply to all or part of general-permit authorizations. Consistent
with 50 CFR part 21 and part 22 permitting, Tribes or States may choose
to be more restrictive than Federal regulations. Permittees must comply
with Tribal and State laws and regulations to be in compliance with
Federal eagle permits.
Eagle Incidental Take Permits for Wind Energy
With this rulemaking, the Service seeks to implement efficiencies
in authorizing incidental take associated with wind energy projects.
This final rule creates a general permit option for projects in areas
that are low risk to eagles. We also revise the specific permit process
to provide clarity to applicants and ensure processing is efficient and
consistent with the preservation standard. With broader participation
in permitting, the Service anticipates increased benefits to eagle
populations as more projects implement avoidance, minimization, and
mitigation measures.
The Service uses a combination of eagle relative abundance and
proximity to eagle nests as eligibility criteria for wind energy
general permits. The Service uses the Cornell Status and Trends
definition of relative abundance and relative abundance products
(Cornell Lab of Ornithology, Ithaca, New York, available at: https://science.ebird.org/en/status-and-trends). Relative abundance values
determined for a project must be based on these publicly available
Status and Trends relative abundance products for bald eagles and
golden eagles. To help project proponents quickly determine eagle
relative abundance, the Service will maintain an online mapping tool
(https://arcg.is/CKLKy1).
For first-time applicants, general-permit eligibility is based on
eagle relative abundance and proximity to eagle nests at the time of
application. All turbines must be located in an area with eagle
relative abundance less than the threshold identified by regulation
(Sec. 22.250(c)(1)(ii) for both bald eagles and golden eagles). All
turbines, including the space occupied by blades or other turbine
infrastructure, must also be located at least 2 miles from a golden
eagle nest and at least 660 feet from a bald eagle nest (Sec.
22.250(c)(1)(i)). Project proponents are expected to survey for eagle
nests with due diligence and in accordance with any Service guidance
for nest surveys.
The Service considered allowing general permit applicants to select
authorization for just one species. By requiring both species, the
Service is able to reduce administration costs and keep the general
permit process simple. Both species are widely distributed and co-occur
in most States. The Service recognizes that the risk to each species is
not uniform, and we factored in the relative risk to each species into
the relative abundance criteria, the nest buffers, and the compensatory
mitigation requirements.
The Service added an eligibility criterion for wind energy projects
that are renewing a general permit (Sec. 22.250(c)). A general
permittee remains eligible to renew their permit, even if the Service
revises eagle relative abundance thresholds or eagles construct a nest
within the species-specific setback distances, as long as the project
remains in compliance with all other general permit requirements. This
includes provisions regarding the discovery of eagle remains or injured
eagles remaining fewer than four eagles of the same species within a 5-
year permit tenure (Sec. 22.210(b)(2)(i)). This eligibility applies to
the turbines authorized under the original general permit and does not
apply if there was a lapse in permit coverage or if any turbines are
added to the project. It does apply if the turbines change ownership.
If a project adds turbines, the new turbines must meet the
qualifications for a first-time general permit (Sec. 22.250(c)(1))
when renewing a general permit for a project. If there is a lapse in
coverage, the project must qualify for a first-time general permit
(Sec. 22.250(c)(1)) and may then renew (Sec. 22.250(c)(2)), if
eligible, or apply for a specific permit.
The Service acknowledges that existing wind projects have less
ability to adapt to the location-based nature of the general permit
eligibility criteria (as defined in Sec. 22.250(b)). After extensive
review, the Service could not identify general permit eligibility
criteria with which a project could self-certify that did not add
extensive complexity or uncertainty. However, the Service retained the
proposed eligibility criterion that any existing project that does not
meet general permit eligibility criteria can submit an application for
a specific permit (Sec. 22.200(b)) and request a letter of
authorization to obtain a general permit (Sec. 22.250(c)). The Service
will review all information provided in the application, including any
site-specific, pre- or post-construction data. The Service will issue a
letter of authorization to apply for a general permit if we determine
that the take rates at the existing project are likely to be consistent
with or lower than eagle take rates expected at similar-sized wind
facilities that qualify for general permits. If an applicant receives a
letter of authorization, we may refund the specific-permit application
fee, but to cover the cost of review, we will not refund the
administration fee. The letter of authorization may require additional
avoidance, minimization, or compensatory mitigation requirements if
appropriate (for example, when needed to ensure consistency with
general permit take rates).
The Service estimates that more than 80 percent of existing land-
based wind turbines in the lower 48 States may be eligible for general
permits. Wind projects in Alaska, Hawaii, island territories, and the
offshore environment should apply for a specific permit if
authorization for eagle incidental take is sought. Authorization for
incidental take due to power line infrastructure is not included under
a general permit for wind. The Service expects wind projects to avoid
risk to eagles by ensuring
[[Page 9923]]
power line infrastructure is avian-safe, either by design or use of
covers. In the rare circumstance associated power line infrastructure
poses an electrocution or collision risk to eagles, authorization under
the power line regulation is most appropriate. Specific permits are
available for wind projects that do not meet general permit eligibility
criteria or request the customization of a specific permit. We have
created multiple tiers within specific permits: Tier 1, Tier 2, and
Tier 2 with reimbursable agreement. Changes to the fee structure
associated with these tiers are described in the Changes to the Fees
section below. Tier 1 specific permits are for low-complexity wind
project applications (1) that can comply with general permit conditions
or require only minor modifications, (2) where fatality estimates can
be calculated with site-specific data collected to Service standards
and submitted using the Service's information reporting template or
where the applicant agrees to use the Service's generalized fatality
estimation process (i.e., using the nationwide specific permit priors)
for specific permits, (3) that agree to use a Service-approved
conservation bank or in-lieu fee program to complete required
compensatory mitigation, and (4) where the Service's decision can be
categorically excluded under NEPA. The Service anticipates expediting
Tier 1 specific permit application processing.
Tier 2 specific permits are for moderately complex applications
that (1) need modifications to general-permit conditions, including
negotiated compensatory-mitigation requirements or (2) for which
fatality estimation requires more evaluation of site-specific data, or
(3) negotiation of other requirements. For the highest complexity
applications, such as applications that require more extensive permit-
condition negotiations, cannot be categorically excluded from
additional procedural requirements of NEPA, or other unique
circumstances, the Service will charge the Tier 2 fee and require
applicants, including government agencies, to enter into a reimbursable
agreement with the Service to offset additional Service costs
associated with this added complexity and review time in excess of 275
hours.
The Service will no longer specify an authorized number of eagles
that may be incidentally killed or injured on the face of general or
specific permits. Permits will authorize the incidental take of eagles.
This means that permittees will not be considered out of compliance for
exceeding an authorized level of eagle take. General permittees,
however, must remain in compliance with the discovered eagle
provisions, which are different from estimated eagle take. However, to
ensure consistency with our preservation standard, we will estimate the
number of eagles taken for internal tracking and calculating
compensatory mitigation requirements. The Service will track estimated
take that has been authorized for bald eagles and golden eagles within
each eagle management unit (EMU) and local area population (LAP). We
will use the best-available information and tools in making these
calculations, including compiling information on discovered eagle
remains and injured eagles, applying statistical modeling to estimate
eagle take that has been authorized under permits, and comparing
estimated take and provided compensatory mitigation with EMU take
limits and LAP thresholds.
The Service received numerous comments regarding the Service-led
monitoring in the proposed rule. The Service reexamined the potential
of using operations and maintenance staff to conduct concurrent
monitoring instead. Ultimately, we decided to reduce the requirement
for general permits to concurrent monitoring because that will still
provide the information the Service requires while resulting in a
substantial cost savings to the regulated community compared to the
proposed Service-led monitoring. The Service intends to publish
monitoring standards for specific permits that will be designed to
maximize flexibility to the regulated community so permittees can
select the best fatality monitoring method for their project, while
still giving the Service the information needed to ensure we are
authorizing take consistent with our preservation standard. Monitoring
must be conducted in accordance with permit conditions and, if
available, Service guidance. The Service may use administration fees to
validate concurrent monitoring methods and analyze concurrent
monitoring data. Under specific permits, additional monitoring may be
included in the permit conditions, such as for permittees wanting to
reduce mitigation requirements by implementing experimental technology
or post-construction monitoring. The Service will require only third-
party monitoring when warranted (e.g., addressing compliance concerns
or applying controversial approaches).
Compensatory mitigation is required for general permits. General
permits must obtain eagle credits from a Service-approved conservation
bank or in-lieu fee program based on the hazardous volume of the
project (Sec. 22.250(f)(7)(ii)). An eagle credit is the amount of
compensatory mitigation needed to offset the take of an eagle. Service-
approved in-lieu fee programs and conservation banks will be authorized
for particular EMUs, consistent with the methodology approved by the
Service. However, the Service will retain the right to direct funds
from an EMU-scale to an LAP-scale, if the Service identifies concerns
with a particular LAP.
Compensatory mitigation is also required for specific permits for
wind energy. Applicants must include their expected method of
compensatory mitigation in the permit application (Sec.
22.250(f)(7)(i)). The Service will derive the amount of compensatory
mitigation required using a project-specific fatality estimate, based
upon either site-specific data that meets the Service's data collection
standards or the Service's generalized fatality estimation process
(i.e., using the nationwide specific permit priors). These priors are
probability distributions, created using information from a range of
projects under Service review and others described with sufficient
detail in Whitfield (2009), that describe exposure and collision
probability in the Service's collision risk model before any site-
specific information is taken into account. All compensatory mitigation
for golden eagles must be performed at a 1.2:1 (mitigation:take) ratio.
The Service expects Tier 1 specific permits to use a Service-approved
conservation bank or in-lieu fee program to meet mitigation
requirements. Tier 2 specific permit applications may use a Service-
approved conservation bank or in-lieu fee program or submit a plan to
the Service for implementing compensatory mitigation consistent with
Sec. 22.200 and Service-wide mitigation policies. To ensure
consistency with the preservation standard, wind energy projects that
are eligible for general permits but choose to obtain a specific permit
will be required to meet or exceed the general permit mitigation
requirements. Compensatory mitigation is not required for wind turbine
infrastructure that is considered baseline. Baseline, as described in
the 2016 PEIS, refers to infrastructure that existed and was operating
in its current configuration and size prior to September 11, 2009.
The Service retains the maximum 30-year tenure for specific permits
for wind projects. This tenure is appropriate given the amount of time
that wind energy projects typically operate on the landscape. Specific
permits may be requested and authorized for any duration (in 1-year
increments) up to 30
[[Page 9924]]
years. General permits for wind projects are valid for 5 years from the
date of registration. Upon expiration of general permits, project
applicants may reapply and obtain a new 5-year general permit. General
permits for eagle take cannot be amended during each 5-year term.
For both general and specific permits, the Service will continue
requiring implementation of all practicable avoidance and minimization
measures to reduce the likelihood of take. These conditions would
likely include reducing eagle attractants at a site (e.g., minimizing
prey populations or perch locations), minimizing human-caused food
sources at a site (e.g., roadkill, livestock), and implementing
adaptive-management plans that modify facility operations at a site if
certain circumstances occur, such as when a certain number of eagle
mortalities are detected. General permit conditions will be
nonnegotiable and fixed for the term of the permit. Renewed general
permits will have the most current version of general permit
conditions. Specific permit conditions will use the general permit
conditions as a foundation but may be modified or added to as
appropriate. The appropriate fee tier will be charged based on the
amount of negotiation and modification required.
Permittees must train relevant employees to look for, recognize,
and report eagle take as part of their regular duties. Permit
conditions will specify a minimum frequency required (e.g., once every
3 months) and require that trained employees visually scan for injured
eagles and eagle remains while in the vicinity of project
infrastructure. Permit conditions will direct disposal (e.g., shipped
to National Eagle Repository) and reporting (e.g., summary emailed to
the Service) requirements and timelines.
When three or four eagles of one species are discovered within the
general permit tenure, we require additional conditions. If three
eagles of one species are found, the permittee must notify the Service
and implement an adaptive management plan. If a fourth eagle of that
same species is found, these steps must be repeated, and the project
would no longer qualify for future general permits. The discovered-
eagles provision aids in identifying the rare project eligible for a
general permit but experiencing more take than other projects covered
by general permits. By requiring notification from projects operating
under general permits if three and four eagles are found, we ensure
that the overall take authorized by the general-permit program remains
within the range we predict and is appropriately offset to the degree
necessary for the preservation of each eagle species. It is important
to note that found eagle remains at any project represent only the
minimum number of eagles that may have been killed by a project.
Depending on the probability of detection, which is determined by
factors like site topography and vegetation, the number of eagles
actually taken may be close to the number of eagles found, or the
number actually taken could be substantially higher.
We will allow time for project proponents to adjust to these
amended regulations. Project proponents who have submitted a permit
application will have 6 months from the publication date of the final
rule to choose whether to have their application reviewed and
administered under all the provisions of the prior regulations, as
amended in 2016, or all the provisions of the current regulations. Any
application fees paid prior to the publication date of the final rule
may be used to pay for application and administration fees required
under the new regulations. However, the Service will not refund any
application fees paid prior to the publication date of the final rule
because the Service will have already undergone substantial processing
of the application. Project proponents who hold a permit under the 2016
regulations may continue under that permit's conditions until the
permit expires. Permittees that want to modify existing permits to
comply with current regulations may contact their permitting office to
determine if a substantive amendment request or a new application is
most appropriate.
Eagle Incidental Take Permits for Power Lines
Power line entities have expressed interest in obtaining
authorization for eagle incidental take caused by powerline
infrastructure; however, a number of barriers have limited
participation in permitting. We create a general permit option for
power line entities that can comply with standardized conditions. We
also revise the specific permit process to provide as an option for
power line entities that require more customization. The Service
anticipates increased benefits to eagle populations as more power line
entities obtain permits and implement required avoidance, minimization,
and mitigation measures.
All power line entities are eligible for general permits. The
Service recommends a general permit for any power line entity that can
comply with standardized general permit conditions. Specific permits
are available for power line entities that seek customized permit
conditions. We have created multiple tiers within specific permits:
Tier 1, Tier 2, and Tier 2 with reimbursable agreement. Tier 1 specific
permits are for low-complexity applications that require minor
modifications to the general-permit conditions and where the Service's
decision can be categorically excluded under NEPA. The Service
anticipates expediting Tier 1 application processing. Tier 2 specific
permits are for moderately complex applications that can be
categorically excluded from additional NEPA procedural requirements and
need unique or substantive modifications to the general-permit
conditions, such as negotiated compensatory mitigation requirements. In
the rare circumstance a power line application exceeds 275 hours in
review time, the Service will charge the Tier 2 fee and require
applicants, including government agencies, to enter into a reimbursable
agreement with the Service to offset additional Service costs
associated with this added complexity and increased review time
exceeding 275 hours. Exceeding 275 hours is expected only in rare
cases; for example, if the Service's decision cannot be categorically
excluded under NEPA or permit conditions require extensive
negotiations.
The Service will not specify a number of eagles authorized on the
face of general or specific permits. However, the Service will use
annual reports submitted by permittees to estimate the number of eagles
taken for internal tracking and to ensure consistency with our
preservation standard. We will use the best-available information and
tools in making these calculations. The monitoring required for general
permits and most specific permits will be limited to concurrent
monitoring by operations and maintenance personnel while onsite.
Monitoring must be conducted in accordance with permit conditions and,
if available, Service guidance. The Service may use administration fees
to validate concurrent monitoring methods and analyze concurrent
monitoring data. Specific permits may require concurrent monitoring or
additional monitoring.
For both general and specific permits, the Service will require
implementation of all practicable avoidance and minimization measures
to reduce the likelihood of take. To aid in assessing what measures are
practicable to implement, the Service will refer to the Avian Power
Line Interaction Committee (APLIC) suggested practices, including
Suggested Practices for Avian Protection on Power Lines: The State of
the Art in 2006 and Reducing Avian Collisions with Power Lines: The
State
[[Page 9925]]
of the Art in 2012, as well as updated versions or new suggested
practice documents, as they become available. General permits for power
line entities include the conditions listed in Sec. 22.260(d).
Specific permit conditions will use the general permit conditions as a
foundation but may be modified or added to as appropriate. The
appropriate fee tier will be charged based on the amount of negotiation
and modification required.
As part of general-permit conditions, the Service requires power
line entities to develop four strategies: collision response, proactive
retrofit, reactive retrofit, and shooting response, as defined in Sec.
22.260(b). The Service encourages power line entities with an Avian
Protection Plan (APP) to incorporate these strategies into the APP.
However, power line entities may choose to include these four
strategies as part of an APP or as stand-alone strategies.
Collision response strategy describes the process to identify
collision-caused mortality events, evaluate factors, and implement
risk-reduction strategies (see Sec. 22.260(b) and (d)). The Service
expects risk-reduction strategies to be commensurate with future
collision risk. For example, an entity would implement all practicable
risk-reduction strategies for a power-line segment with repeat
mortality events in a high-risk location but for power-line segments
with rare or no known collision events, no action or continued
monitoring may be appropriate.
Proactive retrofit strategy describes how existing infrastructure
will be converted to avian-safe (as defined in Sec. 22.260(b)) within
a set timeline (see Sec. 22.260(b) and (d)). Investor-owned utilities
must have a 50-year proactive retrofit strategy to convert poles in
high-risk eagle areas to avian-safe; therefore, 10 percent of poles in
high-risk eagle areas must be converted during each general-permit 5-
year tenure (Sec. 22.260(d)(2)(i)). High-risk eagle areas occur where
eagles are likely to be present and interact with power line
infrastructure. Conversely, low-risk eagle areas occur where eagles are
not present or unlikely to interact with power line infrastructure,
such as urban areas. Applicants will be responsible for the assessment
of high-risk eagle areas, based on this standard. Other utilities
(publicly owned or cooperative) must have a 75-year proactive retrofit
strategy to convert poles in high-risk eagle areas to avian-safe;
therefore, 7 percent of poles in high-risk eagle areas must be
converted during each permit tenure (Sec. 22.260(d)(2)(ii)). The
Service uses the U.S. Energy Information Administration definitions for
investor-owned, publicly owned, and cooperative utilities. The Service
recognizes that this strategy may take more time than the other
strategies to develop. As a condition of the general permit, general
permittees that do not already have a proactive retrofit strategy will
have 3 years from the effective date of this final rule to develop one.
Reactive retrofit strategy describes how infrastructure will be
retrofit to avian-safe in response to an eagle electrocution or death
(see Sec. 22.260(b) and Sec. 22.260(d)). A total of 13 poles or a
half-mile segment of line must be retrofit. The typical pole selection
is the pole that caused the electrocution and six poles in each
direction. However, if retrofitting other poles in the circuit provides
more benefit to eagles, those poles may be retrofitted by prioritizing
the highest risk poles closest to the electrocution event. Poles
outside of the circuit that caused the electrocution may be counted
towards this retrofit requirement only if all poles in the circuit are
already avian-safe. Converting poles to buried line is an avian-safe
retrofit.
To implement the above strategies, power line entities evaluate the
electrocution or collision incident within 90 days and implement a
response within 1 year of the incident. If extenuating circumstances
occur in implementing the strategies, such as catastrophic weather,
extensive fire, or other event that substantively disrupts power
delivery, the power line entity must do the following: (1) Document and
maintain records of the relevant circumstances, including why
circumstances are extenuating and the plan to implement the delayed
retrofits or collision reduction measures. (2) If implementation of
delayed retrofits or collision reduction measures will extend past the
expiration of the current general permit tenure and the permittee wants
to renew the general permit, notify the Service at least 180 days prior
to permit expiration. (3) If the general permit is renewed, any delayed
retrofits or collision reduction measures must be implemented during
the renewed general permit tenure. Otherwise, the permittee is no
longer eligible for a general permit; however, the permittee may apply
for a specific permit.
Shooting response strategy describes the process the permittee
follows when eagles are found killed or injured near power line
infrastructure to identify if shooting is suspected, communicate with
law enforcement, and identify and implement appropriate shooting-
reduction strategies (see Sec. 22.260(b) and Sec. 22.260(d)). Power
line entities are not responsible for law enforcement of nor liable for
shooting events. At a minimum, power line entities must immediately
contact the Service's Office of Law Enforcement if an eagle is found
killed or injured near power line infrastructure and shooting is
suspected. Where there are repeated shooting events, the power line
entity should develop other strategies, including coordinating with the
relevant land-management agency if the death or injury occurs on
government property. The Service is working with APLIC and others to
develop resources and suggested practices. It is generally assumed that
eagle remains or injured eagles discovered in the vicinity of power
line infrastructure are taken by that power line infrastructure, unless
necropsy or other information proves otherwise.
In addition to the above strategies, power line entities must also
consider eagles in siting and design for new construction and rebuild
projects and ensure that all poles constructed in high-risk areas are
avian-safe, as practicable. This provision is not required if it would
impact human health and safety, require overly burdensome engineering,
or have significant adverse effects on biological, cultural, or
historical resources. Permittees must also train onsite personnel to
scan for and appropriately report discovered eagle remains. Under
specific permits, additional monitoring may be required.
Compensatory mitigation is required for both general permits and
specific permits. General permits must implement a proactive retrofit
strategy (Sec. 22.260(d)(3)). Compensatory mitigation for specific
permits will be determined for each application and included in permit
conditions (Sec. 22.260(e)(2)). The Service will track take that has
been authorized for bald eagles and golden eagles within each eagle
management unit (EMU) and local area population (LAP).
General permits for power line entities are valid for 5 years from
the date of registration. Upon expiration of a general permit, a
project applicant may reapply and obtain a new 5-year general permit.
General permits cannot be amended during each 5-year term. The Service
retains a maximum tenure of 30 years for specific permits for power
line entities. The 30-year tenure is appropriate given the extended
time power line infrastructure is expected to operate on the landscape.
Specific permits may be requested and authorized for any duration (in
1-year increments) up to 30 years.
[[Page 9926]]
Eagle Disturbance Take Permits
More than two-thirds of the eagle-take permits the Service
currently issues are for incidental disturbance by activities conducted
near bald eagle nests. Incidental take by disturbance is different from
incidental take resulting in injury or mortality. To reduce complexity
and improve clarity, this final rule creates a new stand-alone
regulatory section for the incidental take of bald eagles or golden
eagles by disturbance (Sec. 22.280). This regulation revises portions
of the previous disturbance-take regulation (50 CFR 22.80). The Service
retains the existing definition of ``disturb'' (50 CFR 22.6) and
clarifies further what does and does not constitute disturbance take
(Sec. 22.280(b)).
The Service creates general permits for eagle incidental take by
disturbance in Sec. 22.280. The Service uses the standardized approach
to permitting based on the 2007 Activity-Specific Guidelines of the
National Bald Eagle Management Guidelines (hereinafter the
``Guidelines''). Between publication of the Guidelines in 2007 and
nationwide eagle-population surveys in 2018, we estimate that bald
eagle populations have quadrupled in the Lower 48 United States (USFWS.
2021. Final Report: Bald Eagle Population Size: 2020 Update. December
2020. Division of Migratory Bird Management, Washington DC U.S.A.).
This includes growth into environments that are developed or in the
process of being developed, increasing the demand for permits for eagle
disturbance. By creating general permits, the Service will better align
the conservation value gained from permitting with ensuring the
preservation of eagles. We estimate about 85 percent of projects that
cause disturbance will qualify for general permits.
General permits are available for the disturbance of bald eagles
when the disturbance will be a result of one or more of the following
activities: building construction, linear infrastructure construction
and maintenance, alteration of shorelines and water bodies, alteration
of vegetation, motorized recreation, nonmotorized recreation, aircraft
operation, prescribed burn operations, and loud intermittent noises.
General permits cover conducting the activity, as well as pre-
construction work, including geotechnical work. The Service did not
include prescribed-burn operations in the proposed rule because, at the
time, we considered such activities part of alteration of vegetation.
However, after considering public comment on the issue and to ensure
clarity for the regulated community, we included prescribed burning as
a potential disturbance activity in the final regulation. Prescribed
burning includes the footprint of the burn as well as where biproducts
of the burn will be present, such as smoke, ash, or embers. Specific
permits are available for disturbance to bald eagles from activities
that are not eligible for general permits and any activity that may
result in disturbance to golden eagles.
The Service specifies distances in the regulation within which
these activities may cause disturbance. Activities occurring farther
than the distances specified below do not require a permit because they
are unlikely to cause disturbance. Regularly occurring activities that
occur within these distances and pre-date an eagle pair's selection of
a given nest site are assumed tolerated by the eagles, unlikely to
cause disturbance, and do not require a permit.
Tribes communicated concern about the issuance of general permits
for nest disturbance and nest take on lands of Tribal interest. In
response, the Service has restricted eligibility, and general permits
are not available for nest disturbance or nest take for nest structures
located in Indian country, as defined in 18 U.S.C. 1151. The Service
considers the case-by-case review of specific permits appropriate for
nests located in Indian country. This restriction does not apply when
the Tribal government is the applicant for the permit on their own
land.
Hazing--the use of nonlethal methods to disperse eagles away from a
site--does not constitute eagle disturbance unless it is adjacent to an
in-use nest and disrupts eagle breeding activity. The intent of hazing
is to deter eagle depredation (e.g., substantial injury to wildlife or
agriculture) or reduce threats to human or eagle health and safety by
temporarily displacing individual eagles from a location. We currently
recommend nest buffers of 660 feet for bald eagles and 1 mile for
golden eagles.
The Service also considers activities that are conducted adjacent
to a communal roost or foraging area do not constitute eagle
disturbance and do not require a permit. ``Communal roost site'' and
``foraging area'' are defined by regulation (50 CFR 22.6). Removal of a
foraging area has greater potential to cause disturbance; therefore, we
further clarify here that activities that completely prevent the use of
a foraging area may cause disturbance. A proponent of a project likely
to fully prevent the use of a foraging area should apply for a specific
permit, particularly if the activity will remove all foraging
opportunities within 1 mile of an in-use nest.
The Service will require monitoring eagles under general and
specific disturbance-take permits. Monitoring will typically consist of
collecting information sufficient to determine whether nestlings have
fledged from the nest. Specific permits for disturbance may require
monitoring as long as necessary to determine any impacts to the eagles
for which take is authorized, including up to 3 years after permit
tenure. The Service does not require compensatory mitigation for
general permits. Compensatory mitigation may be required for specific
permits to ensure the preservation of eagles. For example, any
disturbance take of golden eagles that is not part of the Service's
previously established 2009 baseline or disturbance take of bald eagles
that exceeds the LAP authorized-take threshold and is otherwise
unsustainable requires implementation of compensatory mitigation.
Monitoring, and if required, compensatory-mitigation outcomes must be
reported annually.
For both specific and general disturbance permits, we will require
that applicants provide the coordinates of the nest(s) for which they
are requesting disturbance authorization. Precise location information
is necessary for both the Service staff who conduct eagle-population
management and law enforcement. For disturbance take, we retain a 5-
year tenure for specific permits and implement a 1-year tenure for
general permits. These permits are renewable in the rare circumstance
that an activity is likely to cause disturbance to eagles over a long
period of time. In the rare event that the Service's decision to issue
a disturbance specific permit cannot be categorically excluded under
NEPA, a reimbursable agreement may be used to cover costs associated
with the preparation of an environmental analysis and compliance with
the procedural requirements of NEPA.
For both specific and general permits, we require permit conditions
that include implementation of measures to avoid and minimize, to the
extent practicable, the risk that authorized activities may disturb
eagles. To determine practicability, the Service will consider eagle-
population status, the known efficacy of the measure, and the potential
burden on the permittee. For specific permits, applicants will have the
opportunity to provide input into these permit conditions. General-
permit conditions will be standardized by activity type based on
effective
[[Page 9927]]
techniques that have been consistently and successfully used in
specific permits for the past 10 years or more.
The Service uses this rulemaking to clarify that the regulations
for disturbance take of eagles will be used to authorize the incidental
take of eagle nests. Incidental take of nests caused by activities
includes actions that agitate or bother eagles to a degree that
interferes with normal breeding and sheltering behavior. For example,
prescribed burns may result in the disturbance of breeding eagles
through smoke exposure and may disrupt breeding activity by
unintentionally taking nests when a fire moves unexpectedly across
break lines or into tree canopies. Authorization is provided only for
incidental take of nests that occurs after application of all
practicable avoidance and minimization measures. Incidental take
authorization does not include take caused by lack of due diligence or
negligence; for example, failure to identify nest locations prior to
conducting an activity.
To date, incidental take of nests has been a rare issue and,
therefore, is currently most appropriately addressed under specific
permits. However, the Service will regularly review this issue with
other implementation decisions. Applicants requesting incidental take
of nests must demonstrate that incidental nest take cannot be
practicably avoided. The Service does not anticipate authorizing the
incidental take of nests for development activities. In the Service's
experience, developers have sufficient knowledge of the landscape and
control of their activity to make incidental nest take practicably
avoidable during development.
Eagle Nest Take Permits
The Service has revised the regulations for eagle nest take (Sec.
22.300). This final rule creates a general permit for the take of bald
eagle nests in certain circumstances. We retain specific permits for
the take of any golden eagle nest as well as for the take of bald eagle
nests that is not eligible for a general permit. We also clarify that
relocation or obstruction of a nest constitutes nest take.
We retain the four justifications for authorizing eagle nest take,
which are emergency, health and safety, removal from human-engineered
structures, and other purposes. We also add protection of species on
the List of Endangered and Threatened Wildlife (Sec. 17.11) as a
purpose for eagle nest take. General permits are limited to bald eagle
nest take for the purposes of emergencies, protection of health and
safety, and protection of human-engineered structures. In Alaska only,
bald eagle nests may also be taken for other purposes. After more than
10 years of issuing permits to remove bald eagle nests, the Service has
developed standard permit conditions that can be applied to authorizing
the take of bald eagle nests using general permits for these purposes.
We will continue to require specific permits for any take of golden
eagle nests because these situations have unique conditions that
require site-specific permitting and because of the population status
of golden eagles. We will also continue to require a specific permit
for take of bald eagle nests under the ``other purposes'' in the lower
48 States because the Service must ensure that those permits provide a
net benefit to eagles. The net-benefit determination depends on the
circumstances of the purpose requiring nest take. In Alaska, general
permits are appropriate because the Service has already developed and
implemented standard conditions there and Alaska has a robust bald
eagle population.
In this rulemaking, the Service adds a fifth justification for
authorizing the take of eagle nests when necessary for the protection
of species on the List of Endangered and Threatened Wildlife (Sec.
17.11) under the Endangered Species Act of 1973, as amended (16 U.S.C.
1531-1544). This activity would require a specific permit issued only
to a Federal, State, or Tribal agency responsible for implementing
actions for the protection of the species of concern. With expanding
bald eagle populations, the Service anticipates an increase in
situations where bald eagle management may be a necessary part of
implementing recovery plans.
The Service will not require monitoring for general permits. After
more than a decade of annual monitoring reports, we expect a 1-year
permit tenure to better capture the necessary information to meet the
preservation standard than requiring monitoring. In addition, a 1-year
permit term without required monitoring is less burdensome to the
applicant. Specific permits may require monitoring--for example, a
permittee may need to monitor the area near where a nest was removed
for one or more seasons to determine whether the affected eagles
relocate and successfully fledge young. To be conservative, we will
assume that each nest take authorized by the general permit will result
in a loss of breeding productivity for one breeding season. We may
change this practice in the future if data warrants a change in our
assumption.
The Service will not require compensatory mitigation for nest-take
general permits, unless it is for other purposes in Alaska where
compensatory mitigation is required to achieve the associated net
benefit. General permits for nest take are limited to bald eagle nests
in situations that are typically hazardous to eagles or where eagles
benefit from resolving the situation requiring the permit. Compensatory
mitigation is also not generally warranted for nest-take general
permits because of the improving population status of bald eagles.
Compensatory mitigation may be required for specific permits. In
determining compensatory mitigation, the Service will consider the
purpose for the nest take, whether nest take reduces risk to eagles,
and the population status of the species. A specific-permit applicant
may meet this requirement by obtaining the Service-approved number of
eagle credits from a Service-approved conservation bank or in-lieu fee
program. The applicant may also propose other types of compensatory
mitigation for Service approval.
For both specific and general nest take permits, we will require
that applicants provide the coordinates of the nest(s) for which they
are requesting take authorization. Precise location information is
necessary for both the Service staff who conduct eagle-population
management and law enforcement. The permit application may also require
supporting documentation for certain types of requests (for example, an
arborist report in the case of hazard-tree removal).
For nest take, we retain the 5-year limit for specific permits and
implement a 1-year limit for general permits. These permits are
renewable. The Service considered providing for a longer general-permit
tenure; however, doing so would require that the Service require
further monitoring from all general permittees that was inconsistent
with the purpose of general permits. We have crafted these reduced
tenure and permit-per-nest requirements to better ensure general
permits for nest take are compatible with the preservation of eagles.
Permit conditions will include the applicable regional-breeding-
season start date. Additionally, the general permit will authorize the
removal of a specific nest. General permits may authorize bald eagle
nest removal from the nesting substrate at the location requested and
the location of any subsequent nesting attempts by the eagle pair
within one-half mile of the location requested for the duration of the
permit if the subsequent nest re-
[[Page 9928]]
creates the emergency, safety, or functional hazard of the original
nest. Take of an additional eagle nest more than one-half mile away
requires an additional permit.
Changes to Definitions and Procedures
As part of this rulemaking, we have narrowed the definition of
``eagle nest'' to exclude nest structures on failed nesting substrate.
Previously, we defined ``eagle nest'' to mean any assemblage of
materials built, maintained, or used by bald eagles or golden eagles
for the purpose of reproduction. We have added a qualification that it
must be possible for eagles to reuse the nesting substrate for breeding
purposes. Nesting substrate that, due to natural circumstances, is no
longer and will never again be available to eagles for functional use
will no longer meet the regulatory definition of an eagle nest. This
definition of ``eagle nest'' does not allow for modification of
alternate (unused) nest substrate to a degree that prevents future
breeding activity. These activities will continue to constitute nest
take.
We revise this definition to address uncommon but occasional
instances in which eagle nests or nesting substrate are impacted by
weather or other natural factors to such a degree that they become
permanently unusable to eagles for reproductive purposes. For example,
if a nest tree falls and the bald eagle nest retains its structure, the
nest would no longer retain the official designation of an eagle nest
as the substrate was substantively changed by the nest tree falling. A
permit is not necessary for individuals and organizations to destroy
and remove materials that formerly held the designation of an eagle
nest but no longer meet the definition. However, individuals and
organizations may not collect these materials nor possess them beyond
what is necessary to dispose of the nest. Eggs, feathers, and other
eagle parts are often naturally incorporated into nests with time. The
Eagle Act prohibits possession, transportation, and sale of these
items, either individually or in their incorporated state with former
nesting materials, without Federal authorization.
We also have revised the definition of ``in-use nest'' to clarify
that the eggs referred to in the definition of in-use nest must be
viable. As with our revision of the definition for ``eagle nest,'' this
change ensures that our definition is more relevant to what is
biologically important to eagles. Nonviable eggs may persist in a nest
or even become incorporated into a nest's structure. However, by their
nature, these eggs will not hatch. Under previous definitions,
permittees have been prevented from removing what is otherwise an
alternate nest because of the presence of nonviable eggs outside of
breeding season. In implementing the revised definition, the Service
presumes that eggs are viable unless the applicant provides evidence to
document otherwise (e.g., absence of adults for several days, presence
of eggs out of breeding season).
For clarity, we add a definition of ``general permit'' to 50 CFR
part 22 to distinguish general permits from the definition of
``permit'' in 50 CFR 10.12. We interpret the statutory language
requiring a permit to be procured from the Service for take of bald
eagles for any purpose to include general permits set forth in this
document as well as the more typical individual or specific permits
(see 16 U.S.C. 668a).
We clarify in the regulation pertaining to illegal activities (50
CFR 22.12) that obtaining an eagle permit of any type for a continuing
activity does not in and of itself resolve take that occurred before
issuance of the permit. This provision is currently in Sec.
22.80(e)(8) but applies to all of the regulations in part 22 and is
therefore better located in Sec. 22.12. We also have updated the
definition of ``eagle management unit'' and include a definition of
``incidental take'' to improve transparency to the public and general-
permit applicants.
Along with this final rule, the Service will also implement the
three following changes to our implementation of incidental-take
permits for eagles. We will apply the baseline take for golden eagles
established in the 2009 EA nationwide. Currently, baseline take for
golden eagles is limited to only west of the 100th meridian. In the
2016 PEIS, the Service conservatively assumed that all authorized take
of golden eagles east of the 100th meridian should require compensatory
mitigation regardless of whether the authorized take was occurring
prior to September 11, 2009, and was considered part of the baseline.
However, recent information on the population status of golden eagles
in the Eastern United States demonstrates that this conservative
restriction is not necessary to ensure that take of golden eagles is
compatible with the preservation standard, so we are eliminating this
unnecessary restriction.
We will also update the number of bald eagles debited from EMU take
limits and LAP thresholds when authorizing nest disturbance, based on
new information. Before this change, the Service assumed a loss of
productivity equivalent to 1.33 bald eagles per year for each
authorized nest disturbance in the United States, except in the
Southwest, where we assumed a loss of 0.95 bald eagles per year. Based
on recent Service analysis of new information, we will update the
nationwide debit from 1.33 to a value of 0.26 bald eagles per year.
However, because of low sample sizes in our analysis, we are not
updating the debit in the Southwest, which will remain at 0.95 bald
eagles per year.
Finally, we will remove the 10 percent threshold for unauthorized
mortality in a local area population (LAP) that was introduced with the
2016 rulemaking. We have since concluded that georeferenced data on
unauthorized eagle mortalities are sparse and biased, making meaningful
evaluation and application of unauthorized take at the LAP scale
difficult or impossible.
Changes to Fees
The Service charges application fees to cover the costs of
administering regulations and permits. This includes paying for staff
to: provide technical assistance and guide applicants through the
permitting process, review application information, assess the
biological impact and environmental effects of the proposed activity,
and evaluate whether the applicant meets eligibility and issuance
criteria. For specific permits, these actions are primarily conducted
before permit issuance. For general permits, these actions will be
conducted as part of an auditing process to ensure applicants are
correctly interpreting eligibility criteria and complying with permit
conditions and requirements. Fees are also used to pay for developing
and maintaining an online permit-registration system and database.
General-permit fees include an administration fee. In response to
public comments, the Service adjusted the administration fee to reflect
the elimination of the proposed Service-led monitoring. Instead, the
administration fee will be used to maintain and ground-truth the permit
program to ensure it is compatible with the preservation of eagles,
including to: (1) better understand eagle population dynamics,
including the risk to eagles from authorized activities; (2) better
understand mitigation outcomes, including researching and validating
avoidance, minimization, and compensatory mitigation measures; (3)
address and improve various components of the eagle permitting program,
including gathering and analyzing demographic data, GPS tagging and
tracking eagles for programmatic monitoring, and researching and
validating monitoring
[[Page 9929]]
measures. Some portion of the administration fees may also be used, as
necessary, to fund Service staff time to manage and implement the
general permit administration fees. Specific-permit fees also include
an administration fee. We will use the administration fee for specific
permits for the same purpose as application fees--to fund staff for the
administration of specific permits, including environmental review and
support of the online permit system and database.
The permit fee and administration fee must be paid at the time of
application. We consider permit renewals to be permit applications for
fee purposes. General permits cannot be amended. However, specific
permits may be amended during their tenure. There are three types of
amendments. Administrative amendments are administrative changes,
including name and address information. Consistent with Sec.
13.11(d)(5), there is no fee charged for administrative amendments.
Substantive amendments are those that pertain to the purpose and
conditions of the permit. Consistent with Sec. 13.11(d)(5), we will
charge an amendment fee. The Service will charge an amendment fee and
an administration fee for permittee-requested substantive amendments
that require new analysis, such as modifications that result in re-
estimating take, re-evaluating compensatory mitigation requirements, or
requiring additional environmental review to comply with procedural
requirements under NEPA (Sec. 22.200(e)).
For general permits, the Service adopts a scaled administration-fee
structure to accommodate different sizes of projects. For power lines,
general-permit administration fees are separated into Tier 1 for non-
investor-owned and Tier 2 for investor-owned. The Service uses the U.S.
Energy Information Administration's definition of investor-owned
utilities as ``large electric distributors that issue stock owned by
shareholders'' (https://www.eia.gov/). For wind energy, general-permit
administration fees are separated into Tier 1 for distributed and
community wind projects and Tier 2 for utility wind projects. We use
the Service's Land-Based Wind Energy Guidelines definition of these
terms (https://www.fws.gov). The Service may revise the interpretation
of these terms in future rulemakings.
The Service retains the existing tiers of commercial and
noncommercial for disturbance and nest-take permits. Applications are
commercial, unless (1) an individual applies using section A of the
application form for activities on that individual's privately owned
property for individual purposes, or (2) a government or not-for-profit
entity applies for take associated with public property using section B
of the application form and includes documentation demonstrating its
qualifying status (e.g., documentation that the entity is a government
agency or that the entity is a current, recognized nonprofit
organization by the Internal Revenue Service (IRS) as described in
section 501(c)(3)).
For specific permits, the Service estimates a wide range of
potential permit costs. Costs would vary based on factors like the
complexity of the application or the required environmental review. To
accommodate this wide range, the Service includes a tiered fee
structure in Sec. 13.11(d) and describes criteria for each tier in
Sec. 22.200(c)(2)(vii) and below. For incidental take, the Service
will charge a Tier 1 application fee when specific-permit conditions
require negligible modification from the standardized general-permit
conditions, including the use of a Service-approved in-lieu fee program
or conservation bank for compensatory mitigation. Tier 1 permits would
require Service staff to review and evaluate the application and
coordinate internally prior to permit issuance. We do not anticipate
requiring additional environmental compliance review under NEPA for
Tier 1 specific permits beyond documenting that the action is within
the scope of the existing 2016 PEIS and the 2023 EA issued with this
rulemaking. For wind energy or other applications that require a
fatality estimate, Service estimation of expected take must require
minimal data manipulation; for example, the applicant collects site-
specific data according to Service standards or adopts the Service's
generalized fatality estimate (i.e., using the nationwide specific
permit priors).
The Service will assess a Tier 2 fee for specific permits of
moderate to high complexity that cannot or do not wish to meet the
requirements for Tier 1. Because Tier 2 applications are more complex,
more staff hours, including higher graded staff, are required to review
application information, assess biological impacts and environmental
effects of the proposed activity, and determine whether the application
meets eligibility and issuance criteria. These projects may include
more complex technical assistance, coordination with other programs or
agencies, and documenting NEPA compliance. We estimate the amount of
staff time to complete these tasks for moderately complex projects will
be 250 to 275 hours per permit based on processing times for similarly
complex permits issued by the Service.
We retain the provision in Sec. 13.11(d)(2) that allows an
applicant to request, and the Service to support, issuance of one
consolidated permit when more than one type of permit is required for
an activity and those permits are issued by the same office. When the
Service supports consolidation, a single specific permit may authorize
multiple activities, for example power lines with nest take or wind
energy with power lines. The Service will develop guidance for
consolidating permits. Because of the automated nature of general
permits that have avoidance, minimization, and compensatory mitigation
requirements developed for each activity, a project proponent would
have to obtain the relevant individual general permits. Therefore,
consolidating general permits is not allowed.
The Service expects specific-permit applicants to diligently pursue
obtaining a permit after applying. We will consider a permit
application abandoned or withdrawn if an applicant does not respond to
requests for information or engage in good-faith negotiations. Once we
consider an application abandoned or withdrawn, the applicant must
submit a new application, including fees, to obtain take coverage for
the activity.
Once effective, under this final rule the Service will not charge
an application fee to government entities, consistent with other
permits issued in accordance with Sec. 13.11(d)(3); the Service will
charge an administration fee to any Federal, Tribal, State, or local
government agency for permits issued under part 22 subpart E. The
Service may also require government agencies to enter into a
reimbursable agreement. This fee is necessary to ensure the permitting
program remains consistent with the preservation of eagles.
Administrative Changes
The Service has made the following administrative changes to the
organizational structure of our eagle-take-authorization regulations to
improve clarity. To reduce confusion, we redesignate the current
subpart C ``Specific Eagle Permit Provisions'' as ``Eagle Possession
Permit Provisions.'' We create a new subpart E pertaining to ``Take of
Eagles for Other Interests.'' This subpart now houses regulations that
authorize permits for the taking of eagles for the protection of other
interests in any particular locality.
We redesignate regulations for permits to take golden eagle nests
for
[[Page 9930]]
resource development and recovery operations from Sec. 22.75 to
subpart E, at Sec. 22.325. We update the section heading as ``Golden
eagle nest take for resource recovery operations'' to clarify that this
regulation applies to resource development or recovery operations as
authorized by 16 U.S.C. 668a. The purpose of this regulation is to
authorize the removal of golden eagle nests that are physically in the
way of resource recovery operations, such as on the cliff wall of a
mine. We do not change the regulatory requirements that any take
authorized must be compatible with the preservation of eagles (newly
designated Sec. 22.325(c)) and cannot be reasonably avoided (newly
designated Sec. 22.325(c)(1)). The take of nests in proximity to
resource development and recovery operations to minimize the risk of
disturbance, injury, or mortality to eagles is authorized under Sec.
22.300. We also redesignate the current regulations at Sec. 22.90
pertaining to permits for bald eagle take exempted under the Endangered
Species Act to Sec. 22.400 in subpart E.
Sequencing of General Permits Registration Availability
To implement the general permits authorized under this rulemaking,
the Service is developing an online general-permit registration system.
After the effective date of this regulation, April 12, 2024, the
Service will implement the general permit registration system in stages
to ensure the technology is working appropriately. General permit
registration for incidental take of eagles by wind energy projects and
by power lines is anticipated to be available starting on May 6, 2024.
General permit registration for disturbance of eagles and take of eagle
nests is anticipated to be available starting on July 8, 2024. In the
event these availability dates change, the Service will provide updated
dates on https://www.fws.gov/regulations/eagle and the ePermits website
https://epermits.fws.gov. Those interested in applying for a wind
energy or power line general permit between the effective date of the
rule and the availability of the registration system may apply by: (1)
completing application form 3-200-71, including sections B-D and the
general permit questions in section E and (2) emailing the complete,
signed form to [email protected]. The Service will reply to
the email with the general permit conditions. Entities must comply with
and are authorized by the general permit conditions until the
registration system is available. Once available, entities will have 10
business days to register for a general permit using the registration
system, including paying fees. Failure to register, once available,
voids the prior coverage granted through the above process.
For those interested in applying for disturbance or nest take
permits, the Service will continue to use specific permits for the
remainder of the 2024 nesting season. For activities starting on or
after September 1, 2024, general permits registration is expected to be
available. However, in the event it is not, the procedure described in
the paragraph above will be used starting July 8th until the
registration system is available.
Compliance With the Endangered Species Act
The general permits addressed in the regulations may not be used
for an activity if implementing the requirements of the general permit
may affect ESA-listed species or species proposed for listing or
designated or proposed critical habitat (e.g., burying a cable to avoid
impacts to eagles would result in effects to an ESA-listed snake or
plant). In those cases, the proponent should apply for a specific
permit and, if appropriate, the Service will conduct an intra-service
section 7 consultation on its issuance of the eagle incidental take
permit. That said, since eagle incidental take permits would authorize
only the incidental take of eagles and not the underlying activity,
except as it relates to implementing the conditions of the permit, the
Service's issuance of an eagle incidental take permit would not serve
as a nexus for ESA section 7 purposes for the underlying activity.
Response to Public Comments
The Service received 203 unique letters, which contained 1,649
individual substantive comments, on the proposed rule. The following
sections contain a summary of the substantive public comments we
received on the proposed rule and our responses. Topics are listed in
alphabetical order. Where appropriate, we explain why we did or did not
incorporate the changes suggested by the commenters into this final
rule. Due to the high number of comments, this summary presents major
themes occurring throughout the comments. Not included are the many
comments providing general support for provisions of the rulemaking.
Likewise, we do not include summaries of any comments providing general
opposition, unless they contain suggestions for improvement. We also do
not respond to comments that we considered to be outside the scope of
this rulemaking.
Audits
Issue. Commenters requested more information regarding the proposed
audit program, including details about the auditing process, required
documentation, and expectations for audited entities. Some comments
expressed concerns with the estimated annual percentage of audited
projects, with many indicating a desire for more projects to be audited
annually.
Response. We are developing internal auditing procedures and
external answers to frequently asked questions on audits. Limited
desktop audits and onsite inspections will be conducted to determine if
a project meets eligibility criteria and whether the permittee is
complying with the regulations and permit conditions. In general,
Service staff will conduct an audit following similar procedures to how
staff currently review a permit application and administer permits.
Audits may include reviewing application materials for completeness and
general-permit eligibility. We will verify required reports were
submitted and review the reports. Any required records, plans, or other
documents will be requested of the permittee and reviewed. If there is
a compliance concern, the applicant will be given the opportunity to
submit additional information to address the concern. If, during an
audit, the Service determines that the permittee is not eligible for a
general permit or is out of compliance with general permit conditions,
we will communicate to the permittee options for coming into
compliance.
The Service has estimated the number of audits that can be
conducted each year based on the expected average time to conduct an
audit and the fee money available to fund staff to conduct audits.
Staff will conduct as many audits as possible with the available funds.
There are many uncertainties right now as to how much staff time is
needed to conduct an audit. We estimate approximately 1 percent of
general permits will be audited each year. If we find general
permittees are providing complete information, audits may go quickly
and more projects can be audited. We will regularly assess the cost-
per-audit and the percentage of projects audited to adjust the fee
structure accordingly.
Avoidance and Minimization Measures
Issue. Several commenters expressed concern with a lack of
specificity in the regulation regarding avoidance and minimization
measures.
Response. The role of regulation is to establish performance
standards,
[[Page 9931]]
whereas the role of permit conditions is to provide specificity on how
those performance standards may be met by each permittee. Overly
prescriptive regulations are difficult to keep current and can limit
innovation. Instead, we will provide permit conditions and other
documents to communicate the Service's recommendations on how to meet
regulatory requirements. Avoidance and minimization requirements for
general permits are based on the most commonly applied and effective
measures learned by the Service from more than a decade of permitting.
Eligibility criteria and the performance standards established in the
regulation conditions can be revised through rulemaking. As information
and technology change, the Service may update our recommendations and
expectations on how eligibility criteria and conditions may be met.
Issue. Some commenters expressed the desire to see permit
conditions that incorporate the use of experimental or emerging
technology to avoid and minimize incidental take by wind energy
projects, including Identiflight Bird Detection System, painting one
turbine blade black, or seasonal restrictions on wind turbine
operation.
Response. The Service supports science and technology that
increases safe eagle passage through wind energy facilities. There is
no restriction on permittees implementing these technologies, which can
be used to meet the performance standards of the regulation. However,
the efficacy of these technologies and the details surrounding their
implementation have not been sufficiently studied to warrant
prescriptive requirements in these regulations at this time. The
Service continues to stay abreast of scientific developments and may
include these types of technologies in future rulemakings if evidence
demonstrates their effectiveness. Specific permit applicants may
request that the Service consider the permittee's use of emerging
technologies when the Service estimates fatality.
Issue. We received requests to include perch discouragers as a
standard avoidance and minimization measure for power line poles.
Response. We did not require perch discouragers as a minimization
measure for power line general permits because the effectiveness is
situation dependent. We encourage the use of perch deterrents where
they may be effective. However, APLIC has moved away from broad
implementation of perch discouragers because devices installed to
prevent perching may provide a substrate to secure nest material, and,
in some cases, may increase electrocution risk (APLIC 2023). Prather
and Messmer (2010) tested several types of perch discouragers and found
no difference in perching on poles with or without discouragers.
However, we support the use of perch discouragers in situations where
it is the best or only option for reducing electrocution of eagles.
Issue. Multiple commenters requested that we create ``no go zones''
or similar restrictions prohibiting the installation of wind turbines
in the most important areas for eagles.
Response. The Service did not create ``no go zones'' because doing
so is outside the scope of the Eagle Act. The Service's authority under
the Eagle Act allows the regulation of incidental take of bald eagles
and golden eagles. Our regulatory authority does not extend beyond that
mandate to prohibit the installation of wind turbines or other
infrastructure. The Eagle Act ensures the preservation of our two eagle
species by protecting the survival and breeding productivity of
individual birds but does not directly mandate protection of eagle
habitat. Consequently, the Eagle Act does not give the Service
authority to prohibit certain types of land use, including development.
Instead, it allows us to influence certain types of land use to reduce
the risk of take of bald eagles and golden eagles, including
disturbance of breeding eagles, and to require avoidance, minimization,
and compensatory mitigation from individuals and entities unable to
avoid taking these species. These features of our regulatory process
are common to both existing regulations and these new regulations.
Climate Change
Issue. The Service received comments regarding the implications of
climate change for this rulemaking and the inclusion of climate change
in the EA.
Response. The Service recognizes the threats that climate change
poses to eagles as well as other wildlife. The Service supports all
actions that address climate change, including renewable energy
development. The Service believes that this rule will help facilitate
the development of renewable energy projects by revising the current
permitting approach for eagle incidental take. The permit framework
developed for renewable projects creates clear expectations for
projects to achieve compliance, in some cases with no direct
interaction with the Service (e.g., general permits). The Service is
balancing the need for regulatory certainty, eagle preservation, and
the need for renewable energy development to combat climate change.
While we intend the changes to the eagle-permit regulations to
encourage more projects to apply for a permit, we expect that this
rulemaking will have no impact on the number of future renewable energy
projects on the landscape and, thus, no impact on the trajectory of
climate change.
Compensatory Mitigation
Issue. The Service received numerous comments related to
compensatory mitigation requirements, including advocating for
different methods to achieve these requirements, including lead
abatement, carcass removal from roads, and habitat enhancement.
Response. The Service is actively working on reviewing and
approving other forms of mitigation and encourages potential mitigation
providers to submit their proposals. As part of this rule, we created a
new regulation specific to compensatory mitigation to more clearly
signal requirements to the public. Quantifying the benefits of various
compensatory mitigation measures and developing standards for their
application in permitting is complex. To date, the Service has
authorized power pole retrofits and lead abatement as compensatory
mitigation measures. The Service is actively developing other
compensatory mitigation methods, such as roadside carcass removal, that
will decrease eagle mortality or increase eagle productivity. The
Service encourages interested mitigation providers to contact the
Service with ideas on compensatory mitigation methods. The Service
agrees that it is important to develop compensatory mitigation methods
that offset different sources of mortality and have a wider range of
mitigation providers across the country. We will continue to engage
stakeholders and develop additional guidance and standards for
approving mitigation providers. This will include gathering information
to address mitigation measure effectiveness and uncertainty and
establishing appropriate assurances for the durability of mitigation
measures.
Issue. Some commenters expressed concerns with scaling compensatory
mitigation at the Eagle-Management-Unit (EMU) level rather than the
local-area-population (LAP) level.
Response. The final rule retains the requirement to site
compensatory mitigation within the same EMU where the take is
authorized. Authorized take may affect individual eagles that are both
resident and migratory. Banding records have demonstrated eagle
movements within EMUs beyond individual LAPs. Thus, requiring that
[[Page 9932]]
compensatory mitigation occur at small scales (e.g., the LAP scale) may
be limiting the benefits of compensatory mitigation unnecessarily and
doing so at an inappropriate ecological scale. Additionally, limiting
compensatory mitigation options to the LAP scale is currently not
practicable until there are sufficient mitigation providers capable of
supporting every LAP. When compensatory mitigation is required by the
Service to address an LAP concern, the regulation prioritizes
implementing compensatory mitigation in the LAP where the impacts
occurred.
Issue. Several commenters expressed concerns with requiring
compensatory mitigation for bald eagles and indicated this requirement
is not necessary to meet the preservation standard.
Response. The general-permit compensatory mitigation requirement
includes a small portion for bald eagles. This is necessary to ensure
that the general-permit program is consistent with the preservation
standard established by the Eagle Act and implementing regulations.
General permits do not provide for the project-specific review prior to
issuance; therefore, possible LAP effects must be addressed after
issuance. One tool is to require a small amount of compensatory
mitigation from general permittees that the Service can direct to areas
where LAP thresholds are at risk of being exceeded. The rate of this
extra compensatory mitigation is based on bald eagle take predictions,
but the mitigation amounts provided can be used for either species of
eagle. If an applicant does not want to pay this extra mitigation cost,
which the Service expects to be relatively small for each project, the
applicant may apply for a specific permit where project-specific review
would determine mitigation requirements.
Issue. Several commenters proposed a conservation fund or
conservation fee in addition to any required compensatory mitigation.
Response. The Service has numerous authorities that allow it to
charge an entity permit fees and enter into reimbursable agreements.
Funds collected through permit fees and reimbursable agreements are
used to defer the cost of administering the permit program, including,
but not limited to, salary and other staff-related costs and costs to
ensure that issuance of permits is compatible with the preservation of
eagles. Based on suggestions provided in public comments and as
consistent with the use of collected fees, the Service will use these
fees to fund analysis to: (1) better understand eagle population
dynamics, including the risk to eagles from authorized activities; (2)
better understand mitigation outcomes, including researching and
validating avoidance, minimization, and compensatory mitigation
measures; and (3) address and improve various components of the eagle
permitting program, including gathering and analyzing demographic data,
GPS tagging and tracking eagles for programmatic monitoring, and
researching and validating monitoring measures. The Service does not
have express statutory authority under the Eagle Act to require
contribution into a conservation fund beyond these purposes, nor the
specific authority to direct such funds if they were collected.
Changes to Fees
Issue. Multiple commenters suggested that the fees for general
permits were too high and would disincentivize smaller entities from
participating.
Response. In the final rule, the Service has adopted a scaled fee
approach for both general permits and specific permits. For power
lines, general-permit administration fees are separated into Tier 1 for
non-investor-owned utilities and Tier 2 for investor-owned utilities
(using U.S. Energy Information Administration definitions). For wind
energy, general-permit administration fees are separated into Tier 1
distributed and community scale and Tier 2 utility scale, using the
Service's Land-Based Wind Energy Guidelines definitions. For specific
permits, the Service created a tiered fee structure for wind energy and
power line projects consisting of three tiers: Tier 1, Tier 2, and Tier
2 with reimbursable agreement, where a Tier 1 fee is charged for
standard applications and a Tier 2 fee is charged for complex
applications. A reimbursable agreement will be used when processing
time exceeds 275 staff hours. The Service retains the current non-
commercial and commercial tiering for disturbance and nest take
permits.
Coordination With States
Issue. Several commenters stressed the need for the Service to
coordinate with other Federal and State agencies on the issuance of
general and specific permits.
Response. The Service values coordination with Tribal, State, and
Federal partners, and we intend to continue to coordinate and share
information about permits issued. For general permits, we will
regularly be compiling and distributing information on general permits
issued. We have updated the regulation to reflect what information will
be made readily available to partners and the public. For specific
permits, the Service will continue to consult States, Tribes, and other
Federal agencies as part of our normal permitting procedures. In
addition, Department of the Interior disclosure policies (68 FR 52610,
Sept. 4, 2003) under the Privacy Act also provide for routine
disclosures to Federal, Tribal, State, local, or foreign agencies,
including to exchange information on permits granted or denied, to
ensure compliance with all applicable permitting requirements and
obtain advice relevant to approving or denying a permit.
Issue. Some commenters expressed concern about the locations of
eagle nests being shared with the public, while others stated that some
States are prohibited from disclosing nest locations and that the
Service should not require that information on permit applications.
Response. The Service requires precise location information on nest
locations to properly analyze effects to eagles, including LAP effects,
as well as for law enforcement purposes. The Service will take all
available measures to protect eagles and their nest locations. The
Service will continue to coordinate with State wildlife agencies on
these matters.
Issue. We received comments that expressed concerns with the take
of eagles in States where either the bald eagle, golden eagle, or both
are listed as threatened or endangered at the State level. These
comments requested that the Service provide details regarding
coordination with the States with respect to the distribution of
authorized take across individual EMUs, as well as in relation to the
quantification of LAP thresholds.
Response. Federal issuance of a permit does not supersede Tribal or
State protections of a species. Tribes, States, and other Federal
agencies are not required to authorize incidental take of bald eagles
or golden eagles, even if a permittee has obtained a Service general or
specific permit. It is the responsibility of the permittee to ensure
they are in compliance with all applicable laws and regulations. To
support the protection of local populations in this rulemaking, the
Service has retained the existing preservation standard that requires
the Service to determine that permits we issue are consistent with
eagle preservation at the EMU and LAP scales. Under general permits,
the Service will not analyze cumulative take at the LAP scale prior to
general permit issuance. However, the Service will
[[Page 9933]]
review general permits issued and analyze cumulative take at the LAP
scale if an area of concern is identified. States are encouraged to
review the Service's issued permits and submit any information to the
Service that might assist with assessing impacts to LAPs. If the
Service is concerned about the status of any LAP, we can either (a)
direct compensatory mitigation to areas of concern, or (b) suspend the
general-permit program in whole or in part.
Definitions
Issue. The Service received comments on the definition of ``in-use
nest,'' particularly regarding determining egg viability and nests that
are considered under construction.
Response. The purpose of this change is to address the increasing
frequency of instances of bald eagle nest activity outside of the
breeding season, including non-viable eggs in nests outside of breeding
season and nests being maintained outside of breeding season. The
Service agrees with the expressed difficulty of determining if an egg
is viable in the field. Eggs should be assumed viable, unless evidence
proves otherwise. Evidence like the absence of adults for several days
or presence of eggs out of breeding season should be used to assess the
likelihood of an egg being viable. We removed the protections for nests
under construction or under maintenance for bald eagles. The previous
definitions were part of a conservative approach for the recovering
bald eagle that is no longer warranted. These changes are appropriate
and improve consistency between the Eagle Act nest protections with the
Migratory Bird Treaty Act nest protections.
EA Alternatives
Issue. The Service should reconsider Alternative 2 in the draft EA.
Response. The Service did reconsider Alternative 2 and again
concludes it has a high risk of not meeting our preservation standard
if implemented. Under Alternative 2, the regulations would be revised
to include a general permit for land-based wind energy facilities only,
with eligibility based on a project's distance from eagle nests and
compensatory mitigation requirements in the form of a flat, per-project
fee for mitigation. Adopting Alternative 2 is problematic because
neither the Service nor project proponents know where all eagle nests
on the landscape are located. This lack of data reduces our ability to
reliably determine whether a specific wind project is eligible for a
general permit. This situation also adds uncertainty for projects as
well as to any assessment the Service might perform. Considering this,
we expect Alternative 2 would come with the highest risk of
inconsistency with our preservation standard compared to the other
alternatives.
The Service concludes that the general-permit program described
under Alternatives 3 and 4 will best accomplish the dual goals of
increasing participation and increasing conservation for eagles, where
more than 80 percent of existing turbines on the landscape are eligible
for general permits (and the associated benefits of those general
permits) and where paths to a streamlined issuance of specific permits
are described.
The Service also concludes that Alternative 2's flat fee for
mitigation and monitoring may disincentivize smaller projects (e.g.,
tens of turbines) from applying for take permits compared to larger
projects (e.g., hundreds of turbines). The Service estimates that an
average wind project qualifying for a general permit will pay $312,000
in compensatory mitigation under Alternative 2. This is nearly ten
times the estimated compensatory mitigation cost of $37,200 for
Alternatives 3 and 4. Although industry trends may be toward new
construction of larger facilities and consolidated ownership, wind
energy facilities are long lived (usually 30 years or more). Older
facilities will continue to operate and must be considered when
estimating participation in eagle incidental-take permitting and when
considering financial impacts to permittees under Alternative 2
(Section 5.4.5.1 of the Environmental Assessment). Although risk to
eagles from small facilities that are eligible for general permits may
be relatively low, under Alternative 2, those businesses would be more
susceptible to future enforcement actions and associated enforcement
costs in the event of an eagle take if they remain unpermitted due to
the relatively high cost of flat fees.
EA Economic Analysis
Issue. The Service received several comments on our estimated
mitigation costs, with some commenters suggesting our estimates were
too high while others suggested they were too low.
Response. Because compensatory mitigation is provided either by the
permittee or a third party, costs can vary widely. We acknowledge that
the costs estimated for compensatory mitigation under all alternatives
in the FEA are estimates and are likely to vary, perhaps substantially,
across all permitted projects based on the mitigation method selected,
the in-lieu fee program or conservation bank selected, and other
details. These details are difficult to account for in an economic
analysis, but we considered them as accurately as possible based on
current data and our estimated projections. In the FEA, the Service
estimates compensatory mitigation for an average wind energy general
permit to be $37,200. These estimates are based solely on estimates of
compensatory-mitigation costs using power pole retrofits, which are the
only cost estimates the Service currently has available.
Issue. The Service received comments specifically on our cost
estimates for retrofitting power poles under the power line regulation.
Response. We updated the FEA to reflect our assumption that the
proactive retrofit requirements associated with this rule are not
expected to result in additional costs to power line entities. As
stated in section 5.6.5 of the FEA, the Service assumes that power line
entities most likely to apply for a permit are entities that have a
risk of taking eagles and are already retrofitting power poles, thus
already meeting this requirement.
Eligibility--Wind Energy General Permit
Issue. Many commenters expressed concerns with the general-permit
eligibility for wind energy, specifically regarding the distance from
bald eagle nests.
Response. The Service acknowledges the uncertainty that is created
if bald eagles initiate nesting near a project with a wind energy
general permit. Therefore, we revised eligibility criteria (Sec.
22.250(c)) to provide that a general permittee remains eligible to
renew their permit, even if the Service revises eagle relative
abundance thresholds or eagles construct nests within the species-
specific setback distances, as long as the project does not discover
the remains of four eagles of the same species within a 5-year permit
tenure.
Issue. Multiple comments requested that the Service create a
general permit option for existing wind energy projects (as defined in
Sec. 22.250(b)) occurring within the specific permit zone.
Response. The Service acknowledges the unique challenges of
existing projects being subject to new regulations. However, after
extensive review, the Service could not identify a set of general-
permit eligibility criteria that a project could self-certify without
adding extensive complexity or uncertainty. Therefore, the Service
retained and clarified the eligibility criterion that any existing
project that does not meet general permit eligibility criteria can
apply for a specific permit (Sec. 22.200(b)(7) while requesting a
letter
[[Page 9934]]
of authorization to obtain a general permit (Sec. 22.250(c)).
The Service will review all information provided in the
application, including any site-specific, pre-construction or post-
construction data. If we determine that the take rates at the existing
project are likely to be consistent with or lower than eagle take rates
expected at similar-sized wind facilities that qualify for general
permits, the Service will issue a letter of authorization to register
for a general permit. If an applicant receives a letter of
authorization, we may refund the specific permit application fee, but
to cover the cost of review, we will not refund the administration fee.
The letter of authorization may require additional avoidance,
minimization, or compensatory mitigation requirements as needed to
ensure consistency with general permit take rates. The Service
anticipates expediting the processing of these applications.
Issue. Commenters suggested that the Service should allow the use
of site-specific data to determine eligibility for general permits.
Response. The Service recognizes the value in site-specific data.
However, the purpose of general permits is to apply an efficient and
streamlined approach for issuing permits to projects that the Service
can pre-determine pose relatively low risk to eagles. It is not
currently possible to evaluate site-specific data in an automated
manner, which is necessary for general permits. Applicants that prefer
to use site-specific data may apply for a specific permit and request
review for inclusion in the general-permit program as described in a
previous comment response.
Issue. Commenters suggested that existing projects should still
qualify for a general permit even if some of the project's turbines are
within the specific permit zone.
Response. The Service reviewed at length the possibility of
automatically allowing general-permit eligibility for projects that
overlap the boundaries between specific and general permit zones. This
deviation from the proposed rule appears simple but comes with an
increased risk that our general permit program would be inconsistent
with the preservation standard established by the Eagle Act and
implementing regulations. The risk is further increased because the
projects that would be eligible for general permits by partially
overlapping the general-permit zone would very likely create higher
risk to eagles than other projects that fully encompass the general-
permit zone. The Service must choose between addressing that risk by
increasing the mitigation costs for all general permittees or retaining
that all turbines must be in the general permit zone. Because of how
substantive the increased mitigation costs were, the Service instead
provides a mechanism for existing projects to request an eligibility
determination case-by-case as described in a previous comment response.
Issue. Comments noted that many existing projects would not qualify
for a general permit and stated that many of the current deficiencies
with the specific permit program would still be present under the new
regulations.
Response. The Service has developed and will implement a
streamlined approach to specific permits. One approach we considered
and adopted in the final rule was the creation of new tiers for
reviewing specific-permit applications. The purpose of these tiers is
to separate the specific-permit applications that are able to adopt
standardized approaches from those which request more extensive review
and negotiation. Applicants that are willing to accept standard
specific-permit conditions (and do not require additional NEPA
analysis) are eligible for a less expensive application fee and faster
permit-review times.
Eligibility--Relative Abundance Map and Thresholds
Issue. Comments suggested that the relative abundance maps should
indicate levels of risk so developers could choose to avoid the highest
risk areas, or, at a minimum, understand increased mitigation costs
that might be associated with higher risk areas.
Response. The map published with the final rule uses eagle relative
abundance as an index for potential risk. We use relative abundance
data for eagles because the presence of more eagles in a given area at
different times of the year results in more interactions between
turbines and eagles and therefore increased risk of collisions. Thus,
relative abundance data is an effective proxy for determining the risk
of eagle take in a particular location. Although there are only two
levels of risk depicted in this map, it does highlight areas that the
Service has deemed to have relatively high or relatively uncertain risk
to eagles. It is our intent that this map will be used by developers
when siting wind-related infrastructure. As additional data become
available, we will continue to refine our ``risk maps.''
Issue. The Service received numerous comments regarding the use of
eBird Status and Trends relative abundance products to create the
relative abundance map. Some commenters expressed concern that use of
eBird data would underestimate eagle abundance in areas inaccessible to
birders.
Response. The Service recognized that data products from the
Cornell Lab of Ornithology using eBird data is new to many. It is
important to distinguish that the data products the Service is using
are distinct from raw eBird data. We consider the products from the
Cornell Lab of Ornithology to be currently the best available science
for developing a nationwide approach to permitting. We recognize and
acknowledge the uncertainties that are included with this method, such
as areas where raw eBird data has limited reporting. However, the
Cornell Lab of Ornithology eBird Status and Trends relative abundance
products use machine learning to fill in these gaps based on the
models' ability to relate the eBird observations to environmental
predictors derived from global remote sensing data. For example,
reliability of species distribution model predictions can be increased
for unsampled locations and times by relating environmental predictors
to observed occurrences or abundances. This approach allows us to
predict abundance in places that may not be frequented as often (or at
all) by eBird users.
Issue. Several comments suggested we use information from other
datasets (e.g., migration counts, telemetry studies, roost registries,
USGS breeding bird survey, Audubon Christmas Bird Count, and the
Midwinter Bald Eagle Survey) to supplement and improve maps either in
addition to or as part of the eBird models.
Response. The Service agrees that the best information should be
used to determine eagle relative abundance. To implement general
permits, the Service must regulate at the national scale, which is why
this regulation relies on data products from the Cornell Lab of
Ornithology. The Service intends to incorporate other data into our
mapping efforts, as appropriate. However, it will take time to review
each dataset, including its assumptions and biases, and incorporate
those data into mapping efforts in a meaningful way and at appropriate
scales. We welcome additional information and data that could help with
risk mapping and any investment in data integration efforts.
Issue. We received comments requesting that the Service further
stratify relative abundance thresholds according to differences in
geography (e.g., northern and southern for bald eagles and eastern and
western for golden eagles).
[[Page 9935]]
Response. The Service considered further stratification and the
creation of separate relative abundance criteria for each eagle species
preceding the public comment period. However, adding additional strata
would have changed the scale at which the relative abundance is
evaluated and would have added significant complexity to the general
permit program for wind energy facilities. Thus, we elected not to
incorporate these changes.
The Service will update the map and relative abundance thresholds
periodically. In the FEA, we suggested every 5 years or different
intervals if information suggests shorter or longer intervals are more
appropriate. Between updates, the Service will consider any suggestions
for better and more effective ways to map relative eagle abundance.
General Permits
Issue. One commenter indicated that they thought the proposed rule
placed too much emphasis on general permits. Previously, all eagle take
was permitted with specific permits.
Response. This rule emphasizes general permits because that is the
provision that is being introduced with this rulemaking. The Service
has retained the specific permit approach and provisions. In this
rulemaking, the Service has created general permits as an alternative
approach to obtaining eagle take authorization for projects that meet
eligibility criteria. The purpose of general permits is to simplify and
expedite the permitting process for activities for which the Service
has well-established avoidance and minimization measures and that have
relatively consistent and low risk to eagles. The regulations are based
on the well-established avoidance, minimization, and compensatory
mitigation measures that the Service has been implementing as permit
conditions for the past 14 years. This approach allows us to
confidently authorize take consistent with the preservation standard
established by the Eagle Act and implementing regulations without
requiring Service review prior to issuance. We will continue to refine
the general permit approach and incorporate public input on eligibility
criteria for all general-permit categories included in this rule to
ensure that general permits effectively simplify and expedite the
permit process for eligible projects while meeting the preservation
standard.
Issue. Many comments recommended that the Service allow project
proponents to apply for a separate permit for bald and golden eagles,
as opposed to requiring coverage for both species.
Response. In reviewing comments, the Service realized we did not
sufficiently explain in the proposed rule that the mitigation
requirements are specific to that EMU and proportional to golden eagle
abundance in the EMU. Commenters expressed concern that projects in the
East, where golden eagle use of wind projects is seasonal and generally
relatively low, would be paying to compensate for authorized golden
eagle take in the West, where golden eagle use of wind projects can be
relatively high. This is not the case. Projects in the Atlantic and
Mississippi EMU have a lower golden eagle mitigation rate that is
commensurate with the generally lower risk of golden eagle take in
those EMUs. Similarly, projects in the Central and Pacific EMUs will be
required to pay a higher compensatory mitigation rate for golden
eagles, commensurate with the generally higher risk of golden eagle
take there. There is a small amount of additional mitigation required
in all EMUs, to provide funds if a LAP threshold is exceeded and
mitigation is necessary for the program to remain consistent with our
preservation standard. These details are covered in the Final
Environmental Assessment associated with this rulemaking.
Between the proposed and final rule, the Service again analyzed the
possibility of authorizing general permits by species and did not
select that approach at this time. While seemingly a straightforward
request, separating the species introduces uncertainty, which increases
the risk and complexity of general permits. To meet the preservation
standard, the Service estimates general permit mitigation requirements
based on enrollment and has no basis for predicting how many projects
will opt for coverage of one species versus both. The Service would
effectively need to develop separate general permits for each species,
including corresponding eligibility thresholds, eligibility maps,
mitigation costs, and perhaps monitoring standards. In the interest of
keeping general permits easy to apply for and implement, the Service
retained the requirement that all general permits authorize take of
both eagle species. The Service will continue to review this approach
in future rulemaking.
To illustrate the mitigation costs that will be required under
general permits and how they differ across project sizes and across
EMUs, consider two hypothetical projects: one with 30 and one with 100
project turbines, all turbines having a 95.7m rotor diameter. Both
projects are eligible for a general permit and are located in the
Atlantic/Mississippi EMU (where general permit mitigation rates for
golden eagles are the lowest). We will also consider those same two
projects as being eligible for general permits in the Pacific EMU
(where general permit mitigation rates for golden eagles are the
highest). The 30-turbine project in the Atlantic/Mississippi EMU would
be required to mitigate for 0.20 golden eagles and 0.06 additional
eagles (LAP mitigation), or 0.26 total eagles, every 5 years. That same
project in the Pacific EMU would be required to mitigate for the take
of 0.42 golden eagles and 0.06 additional eagles (LAP mitigation), or
0.48 total eagles, every 5 years. The 100-turbine project in the
Atlantic/Mississippi EMU would be required to mitigate for 0.66 golden
eagles and 0.20 additional eagles (LAP mitigation), or 0.86 total
eagles every 5 years. That same 100-turbine project in the Pacific EMU
would be required to mitigate for 1.40 golden eagles and 0.20
additional eagles (LAP mitigation), or 1.60 total eagles every 5 years.
These two hypothetical projects illustrate the relatively low cost
of obtaining golden eagle take coverage for projects that are eligible
for a general permit, and especially the lower cost for smaller
projects and projects in the East, where golden eagle presence is
seasonal and they are generally less abundant than in many parts of the
West. We are hopeful that general permit applicants who think their
risk to golden eagles is low will view this relatively low mitigation
cost as worth the price of incidental take authorization for golden
eagles, in the event such take should occur. If applicants wish to
receive a permit for only one eagle species, they may apply for a
specific permit.
Issue. Several comments expressed concern with regard to potential
suspension or termination of the general permit program, including a
suggestion that suspension or termination should be subject to public
notice and comment prior to finalization.
Response. The Service recognizes the uncertainty that a potential
suspension or termination causes. Suspension or termination of general
permitting is an important aspect to allow the Service to respond
quickly in the event of sudden changes in eagle populations at the LAP
or EMU scale; however, it is not a step the Service would take lightly
and without a notice and comment process.
Regulations currently allow for the revocation of a permit if ``the
population(s) of the wildlife or plant that is the subject of the
permit declines to the extent that continuation of the
[[Page 9936]]
permitted activity would be detrimental to maintenance or recovery of
the affected population'' (50 CFR 13.28(a)(5)). The Service will
regularly evaluate whether the authorized take of bald eagles and
golden eagles under general permits remains compatible with the
preservation of eagles. If the Service finds that issuance of general
permits in a particular LAP or EMU is not compatible with the
preservation of bald eagles or golden eagles, we would first consider
adding additional precautions to the permitting program through
rulemaking. Rulemaking requires public review and comment periods.
However, the Service is preserving, as a last resort, the option of
suspending general permit issuance locally or nationally after
publishing a notice in the Federal Register. This notice may include an
opportunity for the public to comment on next steps. If the Service
suspends general permitting, take currently authorized under a general
permit remains authorized until expiration of that permit, unless the
permittee is notified otherwise.
Issue. Some commenters asked us to explain how ``low effects'' are
determined for general permits.
Response. Public comment indicated that the Service's intent was
not clear in the usage of the phrase ``low effects.'' We have modified
the text to instead reference ``low risk.'' General permits simplify
and expedite the permitting process for activities that have relatively
consistent and low risk to eagles and well-established avoidance,
minimization, and compensatory mitigation measures. For wind energy
facilities, projects that have low risk will be determined by the
relative abundance of eagles and the proximity of wind turbines to nest
locations. For other general permits, the Service considers the
implementation of the well-established avoidance and minimization
measures to result in those projects being low risk to eagles.
Guidance
Issue. Several commenters requested more information regarding
guidance documents that the Service plans to develop.
Response. The Service is working on internal procedures, external
outreach, and guidance documents to help the public understand and
comply with these new regulations. In developing guidance, the Service
will follow standard Federal guidance practices. All regulatory
requirements are included in the rule. Guidance documents provide a
step-down from the rule that explain and clarify the Service's
expectations on how to meet regulatory requirements.
Monitoring
Issue. While many commenters were supportive of the removal of
third-party monitoring, we received comments in support of retaining
this provision.
Response. The third-party monitoring requirement has proven
impracticable or impossible to implement at some projects for a variety
of factors, including health, safety, liability, and access issues for
project sites that are leased from multiple private landowners. These
factors have created a barrier to obtaining a permit. The Service
reviewed the purpose of third-party monitoring and determined in most
circumstances it is sufficient to rely on the requirement that the
permittee must certify that the information submitted is complete and
accurate to the best of their knowledge and belief, subject to criminal
penalty for supplying false information. The Service concluded that the
existing penalties for false reporting under eagle take permits will be
enough to dissuade most permittees from intentionally providing
inaccurate reports. We retain the ability to require third-party
monitoring on a case-by-case basis for specific permits, particularly
if we have ongoing compliance concerns.
Issue. Commenters expressed concern over the amount of money the
Service was proposing to spend on monitoring.
Response. The Service recognizes the tradeoff between spending
money on monitoring or on compensatory mitigation. Monitoring can be
expensive, and it may not be immediately clear how more monitoring
benefits eagle preservation. The benefit of compensatory mitigation is
more straightforward. While extensive monitoring has occurred at
numerous wind projects, it remains difficult to draw programmatic,
cross-project conclusions. Monitoring in a manner that allows for
programmatic conclusions is critical to ensure implementing these new
regulations will be compatible with eagle preservation.
However, based on public comment, the Service reviewed its proposed
approach to monitoring. We determined that we can accomplish monitoring
goals under general permits with concurrent fatality monitoring, which
will be required under general permits, and without additional
monitoring performed by or contracted by the Service. In the final
rule, we require concurrent monitoring conducted according to Service
protocols by project operations and maintenance staff, which will be
sufficient to meet the Service's monitoring needs, provided there is
sufficient participation in wind energy general permitting. We continue
to require an administration fee, a portion of which will be used to
validate the concurrent monitoring approach and analyze monitoring
data.
Issue. We received comments that expressed concern over the removal
of the required 5-year check-ins.
Response. The purpose of 5-year review is to update take estimates
and related compensatory mitigation for the subsequent 5-year period.
It also provides the Service with an opportunity to amend the permit to
reduce or eliminate conservation measures or other permit conditions
that prove to be ineffective or unnecessary. The purpose of these
reviews does not change with this rulemaking. However, the 5-year
requirement has introduced unintended uncertainty which, according to
public comment, has reduced participation in eagle take permitting
under the 2016 regulations. It has also resulted in timing issues,
where post-construction monitoring or other data is available off-cycle
from the 5-year timing (e.g., year 3 or 4) but cannot be used until the
scheduled check-in. Instead, check-ins may now be initiated by the
permittee or the Service in response to events that warrant review, for
example, updating fatality estimates and associated compensatory
mitigation requirements or revising permit conditions to reflect the
best available science.
Issue. We received comments stating that our current surveys are
not sufficient to adequately estimate eagle population numbers and that
mortality data reporting is voluntary and unreliable.
Response. The Service uses the best available science in ensuring
that general and specific permits are consistent with the preservation
of eagles. The Service has conducted aerial surveys for both bald
eagles and golden eagles relatively recently and consider these survey
efforts adequate to estimate populations of both species within
applicable parts of their range. The Service agrees that voluntary
reporting of mortality data is unreliable. With this rulemaking, the
Service improves voluntary reporting at wind projects in two ways.
First, through increasing participation in permitting and prescribing
the concurrent monitoring protocol all projects use, the Service
expects improved quantity and quality of eagle fatality data at wind
projects. Second, through the collection of an administration fee, the
Service can direct funds as needed to ensure permitting is consistent
with the preservation standard, including by
[[Page 9937]]
survey populations and by analyzing project-specific mortality data.
Issue. Commenters felt that monitoring related to disturbance take
and nest take should not be required, specifically in instances where
the activity does not directly take eagles, as with communication
towers.
Response. Unlike permits that authorize the incidental injury or
death of eagles, monitoring required under nest take and nest
disturbance permits is intended to detect breeding outcomes during
current and subsequent nesting attempts and, if appropriate and
practical, document if eagles breed again at their original or any new
nesting location. The loss of breeding productivity constitutes take,
as it prevents eagles from being added to the population. Monitoring
requirements allow the Service to more accurately account for
authorized take against our established species-specific take limits
and, over time, may allow us to qualify or quantify the effectiveness
of permit conditions.
Nest Disturbance
Issue. Comments regarding nest disturbance primarily focused on the
buffer distances set for general permits, including those for in-use
and alternate nests, and advocated for distances based on the level of
tolerance to disturbance.
Response. By specifying distances in our bald eagle nest
disturbance general permit, we are not suggesting that all activities
within these distances must apply for a permit. Rather, we are setting
a standard that only those activities listed within the final rule
(Sec. 22.280(b)) within these distances can receive a general permit.
This standard is intended to prevent project proponents applying for
unnecessary permits for activities beyond these distances that are
unlikely to disturb breeding bald eagles. Further, the specific and
general permits for nest disturbance are not a prerequisite to carrying
out activities or starting projects. Instead, they cover any
disturbance that may result as an unintentional consequence of an
activity. If an individual or entity assesses that their activities are
unlikely to disturb breeding eagles, they do not need the Service's
consent or concurrence to proceed, though they may be held liable if
their activities do ultimately cause disturbance.
The Service acknowledges the growing body of evidence demonstrating
that some portions of the bald eagle breeding population demonstrate
increased tolerance to human activities. Our standards under the nest
disturbance general permit reflect this consideration. We use the 330-
and 660-foot distances for bald eagles because we are generally
unconcerned with activities beyond these ranges, and we discourage
proponents from applying for permits where best available science
suggests they are unnecessary. Within those distances, project
proponents may assess their relative risk to eagles (e.g., whether or
not a similar activity is or has occurred closer to the nest) and
determine whether or not to apply for a permit.
Regarding alternate nests, we agree that, by definition, activities
at these nests cannot expose breeding eagles to sensory disturbance, as
the eagles are not present. However, as the National Bald Eagle
Management Guidelines (2007) note, alterations to the nest site and
surrounding habitat may discourage eagles from breeding when
encountered by eagles returning to that nest site. We will continue to
update the National Bald Eagle Management Guidelines as well as develop
similar guidelines for golden eagles.
Issue. We received requests for a regulatory authorization for
State wildlife agencies for land-management activities that may improve
eagle-nesting habitat, including prescribed fire and mowing.
Response. The Service acknowledges the usefulness of regulatory
authorizations; however, we do not consider regulatory authorizations
an appropriate mechanism to authorize the mortality or injury of bald
eagles or golden eagles at this time. Most land-management activities,
such as alteration of shorelines, alteration of vegetation, and
prescribed burns, are eligible for general permits for eagle
disturbance take. General permits for disturbance caused by
agriculture, mining, and oil and gas operations are not available at
this time. We have received permit requests for these activities
infrequently, thus we have not yet developed standard avoidance and
minimization measures. Operators of these and other activities may
apply for specific permits. As we gain more information on the effects
of these activities and identify effective avoidance and minimization
measures, we may in future rulemakings add general-permit regulations
for these and other activities.
Issue. Commenters asked whether a single general permit authorizes
several types of disturbance or whether a separate general permit will
be needed for each type of disturbance that could occur.
Response. Consistent with our current approach to permitting, a
single permit for disturbance of bald eagle nests can authorize
disturbance of a nest from multiple sources of disturbance of a single
project or operation. For example, a general permit could authorize
disturbance from land clearing, external construction, blasting, and
operations and management activities associated with one project. The
bald eagle nest disturbance permit is a ``one permit, one nesting
territory'' system that simplifies our bald eagle population management
tracking and reduces the amount of monitoring we require from
permittees.
Issue. Commenters also expressed the desire for one permit for all
bald eagle disturbance associated with a given activity for the 5-year
permit term.
Response. Allowing coverage for an unspecified number of nests and
ad hoc accounting of effects would hinder our ability to ensure take is
consistent with the preservation standard established by the Eagle Act
and implementing regulations. Individuals or entities that want to
obtain coverage for disturbance of multiple nesting territories may
apply for a specific permit.
Nest Take
Issue. Comments related to nest take centered on the creation of
general permits and the lack of Service review of those permits.
Response. General permits are generally limited to three scenarios:
emergency circumstances, health and human safety concerns, or nests on
human-engineered structures. These situations, such as wildfire hazard
and structural failure, often pose risks to both the nest and for
people. In these situations, it is often imperative that the permit be
issued as quickly as possible, as doing so often reduces the risk or
effects to eagles. The Service also has been implementing permits for
these activities since 2009 and has well-developed permit conditions
with avoidance and minimization measures. The expedient processing and
standardized approach make these permits a great fit for general
permits.
The Service will review these permits. In reviewing bald eagle nest
take permits at the program scale, given the current and expected
number of permits issued and the status of the bald eagle, the Service
is confident that issuance is consistent with the preservation of the
bald eagle. We will continue to review nest take at the program scale
to ensure that general permit issuance is consistent with the
preservation of bald eagles. The Service will also audit a percentage
of nest take permits, to ensure that the applicants meet eligibility
criteria and comply with permit conditions. We will work to
[[Page 9938]]
address any compliance concerns with individual permittees.
Issue. Some commenters requested that a single general permit for
nest take authorize the take of multiple nests from a single project or
across a defined area.
Response. Issuing one general permit for each nest allows the
Service to efficiently track take. If the Service allowed coverage for
an unspecified number of nests, the associated ad-hoc accounting of
effects would make it much more difficult for the Service to ensure
authorized take is consist with the preservation standard. Specific
permits remain available for the take of multiple nests.
Issue. One commenter stated that the proposed regulation would no
longer require the Service to make a finding of net benefit to eagles
for nest take authorized under ``other purposes.'' The commenter
interpreted the proposed rule to state that compensatory mitigation is
required only when the take exceeds the limit of the applicable EMU.
Response. Since 2009, the regulations require the finding of a net
benefit to eagles for nest take authorized under ``other purposes.''
For all nest-take requests outside of Alaska, a specific permit is
required for the purposes of the Service determining whether a net
benefit will be achieved by the proposed action, or, if the activity
does not provide the net benefit, the compensatory mitigation proposal.
The net benefit to eagles is scaled to the effects of the nest removal.
The Service did include a general permit for ``other purposes'' in
Alaska because of the scaled effects of nest removal. In Alaska, well-
established permit conditions provide sufficient avoidance,
minimization, and compensatory mitigation scaled to the effects of nest
removal, given the robust population status of the bald eagle and the
available nesting habitat.
Issue. Some entities expressed support for the creation of general
permits for golden eagle nest take.
Response. The Service did not include but will continue to work to
develop general permits for golden eagle nest take. The Service has
issued few golden-eagle nest take permits and therefore does not have
sufficient, well-established measures to create general conditions for
golden eagle nest take.
Issue. One commenter suggested that authorizing the take of eagle
nests to protect threatened or endangered species should apply only to
bald eagles due to the golden eagle's population status.
Response. With expanding bald eagle populations, the Service
foresees situations arising where the take of an eagle nest may be
necessary for the recovery of threatened or endangered species.
However, the Service acknowledges the tradeoffs are more complex with
golden eagles. Because this is an emerging issue, a specific permit
must be obtained for this type of activity. The Service added an
additional precaution in that the Federal, State, or Tribal agency
responsible for the species of concern must obtain the permit. The
Service will assess the tradeoffs between the eagle species taken and
the endangered or threatened species. The Service will consider the
evidence that eagles are limiting the recovery of a threatened or
endangered species and analyze whether the eagle nest removal will
improve recovery for the threatened or endangered species in question.
The Service will consider if issuing this permit, including required
avoidance and minimization measures and compensatory mitigation, is
consistent with our preservation standard at both the LAP and EMU
scale. Finally, the Service will consider if other methods are feasible
that have less effect on eagles but will still abate or prevent the
problem. As a final protection for golden eagles, the Service may
require compensatory mitigation for the take of golden eagle nests.
Permit Conditions
Issue. Commenters asked whether the provisions in the new rule
would apply to entities that currently have long-term incidental take
permits and entities that applied but have yet to receive a permit.
Response. Projects that have submitted an application as of
February 12, 2024, will have until August 12, 2024, to choose whether
to have their application reviewed and administered under all the
provisions of the 2016 regulations or all the provisions of these new
regulations. Projects permitted under the 2016 regulations may continue
under existing permit conditions until the permit expires. Permittees
that want to modify existing permit conditions to comply with the new
regulations may contact their permitting office at any time to
determine whether a substantive amendment request or a new application
is most appropriate. For qualifying projects that elect to have their
pending applications reviewed and administered under all the provisions
of these new regulations, application fees paid prior to August 12,
2024, may be used to pay for application and administration fees
required under the new regulations.
Issue. Multiple commenters expressed concerns over operations and
maintenance staff conducting monitoring, suggesting that they might
underreport their findings or that they would find too few available
carcasses to provide useful information on eagle take.
Response. There are two aspects to this concern. The Service
acknowledges the concern about staff intentionally underreporting their
findings. Based on input the Service received, we predict this will be
a rare circumstance and one that can be discovered and addressed with
the assistance of the Office of Law Enforcement. With any permit, there
will be good actors and bad actors, and the Service will address bad
actors accordingly.
For the second aspect, the Service disagrees that concurrent
monitoring will not provide useful information. Service analysis
suggests that, on a large scale (e.g., aggregation of all general
permits), concurrent monitoring will provide sufficient information
over time to allow the Service to be confident that our resulting
program-wide take estimates are consistent with the preservation of
eagles.
Issue. A commenter requested clarification as to when an adaptive
management plan is required.
Response. It is expected that wind energy project proponents will
develop an adaptive management plan prior to or on obtaining a general
permit. However, implementation of the adaptive management plan is
required only if a certain number of fatalities are discovered at a
wind energy facility. If three bald eagle injuries or mortalities, or
three golden eagle injuries or mortalities, are discovered at a project
during the 5-year general permit tenure, the permittee must provide the
Service with an adaptive management plan and specify which avoidance
and minimization measures the permittee will implement. If an injury or
mortality of a fourth eagle of that species attributable to the project
is discovered, the permittee must identify and implement the avoidance
and minimization measures outlined in the adaptive management plan.
Adaptive management plans may be revised during the permit tenure. A
copy of adaptive management plan(s) may be requested by the Service at
any time as part of an audit.
Issue. One commenter asked for clarification whether circumstances
impacting eagles outside of a specific permittee's control (e.g.,
decrease or shift in population due to disease, climatic factors, or
illegal take like poisoning and poaching) could result in
[[Page 9939]]
new obligations being imposed on a specific permit holder.
Response. Circumstances outside the permittee's and the Service's
control will continue to affect eagle populations. The permittee's
responsibility is to comply with the requirements of their permit. The
Service's responsibility is to ensure permits issued are consistent
with the preservation of eagles, including at the EMU and LAP scales.
If situations arise at the EMU and LAP scale that are detrimental to
eagle populations, the Service may need to act to ensure preservation
of eagles, which may include programmatic changes to permits or changes
to a subset of permits. Generally, we will first attempt to address
these issues modifying the requirements for or restricting new permits.
However, consistent with 50 CFR 13.23(b), the Service reserves the
right to amend any permit for just cause at any time during its term,
upon written finding of necessity.
Power Lines
Issue. Comments regarding eagle incidental take permits for power
lines were focused primarily on the required conditions and definitions
in the regulation.
Response. The Service made several improvements to the power line
regulation:
1. To better align with standard industry terminology, the Service
revised the term ``electrocution-safe'' to ``avian-safe.''
2. The Service clarified that power line entities are required to
ensure that all poles constructed in high-risk eagle areas are avian-
safe, allowing the entity to determine those areas within the
parameters provided by Service guidance.
3. To address concerns regarding the siting of projects and buffer
distances, we revised the conditions to read as follows: ``For new
construction and rebuild projects, reconstruction, or replacement
projects, incorporate information on eagles into siting and design
considerations. Minimize eagle risk by siting away from eagle use areas
(e.g., nests and winter roosts), accounting for the risk to and
population status of the species, unless this requirement would unduly
impact human health and safety; require overly burdensome engineering;
or have significant adverse effects on biological, cultural, or
historical resources.''
4. The Service modified the definition of ``collision response
strategy'' to reflect that any risk-reduction strategies implemented
post-collision should be commensurate with the collision risk. This may
include no changes for one-off situations that are unlikely to reoccur.
References to changes in engineering design have been removed and will
instead be included in guidance.
5. Many companies were concerned that the proactive retrofit
strategy would be infeasible to implement. Proactive retrofit
strategies are important, as they serve as the compensatory mitigation
requirement for power line entities. However, the Service also wants to
ensure that requirements are feasible. The Service modified the
requirement to a 50-year strategy for investor-owned utilities and a
75-year strategy for non-investor-owned utilities, with 5-year
benchmarks. We also clarified that this requirement applies only to
poles in high-risk eagle areas that are not avian-safe but may include
other poles in the service area as well. The Service provides for
delayed implementation to allow utilities to develop proactive retrofit
strategies. The Service also provides for extenuating circumstances,
such as catastrophic weather, wildfire, or other events that
substantively disrupt power delivery, in implementing these strategies.
Finally, we note that specific permits are available for any utility
that is unable to implement the general permit requirements.
6. The Service amended the conditions associated with the reactive
retrofit strategy to clarify that the evaluation of the incident must
be completed within 90 days and the response implemented within 1 year
of the incident.
7. The Service clarified that the minimum expectation for the eagle
shooting response strategy is for utilities to notify the Office of Law
Enforcement in the case of a confirmed or suspected shooting. However,
we will work with industry to develop other common-sense response
options.
Issue. Several comments expressed concerns regarding the costs
associated with implementing the avoidance and minimization measures
for power lines.
Response. The fees and costs to applicants to participate in the
permitting framework have been updated and are included in the FEA. See
tables 5-1 (No Action Alternative), 5-4 (Alternative 2), 5-10
(Alternative 3), and 5-14 (Alternative 4). These tables comprise all
fees and costs that a permittee is expected to accrue in applying for
and complying with all permits. As stated in section 5.6.5 of the FEA,
the Service assumes that power line entities most likely to apply for a
permit are entities that have a risk of taking eagles and are already
retrofitting power poles, thus already meeting this requirement.
Therefore, the Service does not anticipate an added cost to power line
entities for the retrofit requirement.
Specific Permits
Issue. Several commenters expressed concerns with delays in
specific permit issuance review and requested that the Service further
streamline the specific permit process.
Response. The Service will be implementing several approaches to
improve efficiency in the specific permit process. One approach
codified in this rulemaking is the creation of new tiers for reviewing
specific permit applications. These tiers separate the specific permit
applications that require extensive review and negotiation from those
that do not, creating a streamlined approach and corresponding reduced
application fee for projects that meet the new Tier-1 criteria.
In addition to creating a tiered approach allowing faster
processing for Tier-1 specific permits, the Service will institute a
procedural change to further expedite review of some projects. To date,
42 eagle incidental take permits have been issued to wind energy
projects across the country. While all permit decisions were analyzed
in an EA or, occasionally, an EIS, our experience with issuing these
permits has led us to conclude that a categorical exclusion would be
appropriate for most permit decisions because relevant environmental
impacts for most decisions have already been analyzed in the 2016 PEIS
and extraordinary circumstances are unlikely to apply, given the
general impacts we disclosed in our NEPA analyses for previously
analyzed decisions. Specific permit decisions we expect to
categorically exclude from further NEPA analysis must, at a minimum,
include the following criteria: (1) Estimated annual eagle take, after
compensatory mitigation (if required), is below EMU take limits; (2)
estimated annual eagle take, combined with other authorized take in the
vicinity, does not exceed five percent of the project-specific Local
Area Population; (3) permit conditions do not have the potential to
cause effects on cultural resources or other historic properties
protected by the National Historic Preservation Act; (4) permit
issuance will not be precedent setting; (5) the permit decision and
permit conditions will not be based on take estimates produced from new
or unpublished methods or models; and (6) no other extraordinary
circumstances that prevent application of the categorical exclusion
exist. If the Service determines categorical exclusion is not
appropriate, the Service
[[Page 9940]]
will initiate an EA or EIS in accordance with NEPA. To ensure linear
and efficient progress, substantive Service work on these documents
will begin after the applicant and the Service have completed
negotiations on the conditions of the permit.
Tribal Concerns
Issue. There were concerns expressed regarding the removal of
protections from Sec. 22.85 of the existing regulations, including the
following:
Evaluation of cultural significance of a local eagle
population;
Finding of a practicable alternative to nest removal;
Finding of a net benefit to eagles and subsequent
compensatory mitigation;
Determination of whether suitable nesting and foraging
habitat is available to accommodate eagles displaced by nest removal;
and
Finding that permits will not preclude higher priorities,
including Native American Tribal religious use.
Response. The Service did not intend to remove the protections
listed above. Many were moved to other sections or condensed with other
regulatory language with the intent to provide clarity. However,
comments indicate this rearrangement did not improve clarity. We have
re-expanded the regulatory language or relocated the language to the
expected locations.
Issue. Several comments from Tribes focused on the creation of
general permits, particularly for nest take and nest disturbance.
Response. Regarding opposition to general permits for nest take and
nest disturbance, the Service notes that these permits are only for
emergencies, for health and safety issues, or on human-engineered
structures. In most cases, these situations are a risk to both eagles
and humans. The qualifications for specific and general permits for
nest disturbance and nest take are comparable to the standards
established in 2016. Additionally, the conditions for our general
permits will be based on the conditions the Service commonly requires
in its current specific nest take and nest disturbance permits. While
we are aiming to make applying easier for project proponents by
simplifying the administrative process, we are not making permits
easier to secure in the sense of relaxing requirements to protect
eagles.
The standards we are establishing around general permits for take
and disturbance of bald eagle nests will assure continued preservation
of this species for two reasons: First, because those standards are
based on the knowledge and experience we have gained from issuing and
monitoring hundreds of permits over nearly two decades, and second, a
growing body of scientific literature has demonstrated that breeding
bald eagles show a higher tolerance and resilience to disturbance and
other impacts than previously thought. We do not have comparable data
or experience in managing golden eagle nests and have therefore not
opened the general-permit program up to removal or disturbance of
golden-eagle nests in this rulemaking.
We acknowledge and appreciate Tribal concerns regarding the degree
of oversight required for general permits when compared to specific
permits. As part of this final rule, we have added a new eligibility
restriction for nest-disturbance and nest-take activities in Indian
country, as defined in 18 U.S.C. 1151, after recent consultation with
Tribes. General permits will not be available for nest take or nest
disturbance for nest structures located in Indian country, unless
requested by the Tribe itself. Furthermore, the Service will make
publicly available a list of all general permits issued, which Tribes
can review. We will be implementing an audit program to ensure that
those participating in our general permits are truly eligible and are
complying with the permits' terms. For specific permits, the Service
will continue to notify Tribes regarding activities conducted on their
lands.
Issue. Many Tribes believe the new regulations remove opportunities
for Tribal engagement and bypass government-to-government consultation,
especially for potential impacts to Tribal lands or resources.
Response. Throughout all phases of the rulemaking process, the
Service has encouraged and continues to welcome government-to-
government consultation. In addition, we conducted multiple information
sessions specifically for Tribes. The Service acknowledges our Federal
Tribal trust responsibilities and deeply honors our sovereign nation-
to-nation relationship with Tribes. To date, one Tribe requested
government-to-government consultation regarding this regulation. The
Service made modifications to the final rule based on this
consultation. We invite bilateral government-to-government consultation
at any time.
Wind Energy
Issue. Some commenters expressed concerns about the cumulative
impacts of wind energy projects on the landscape on eagle populations,
particularly at the LAP scale.
Response. The Service has considered at length how to implement
general permits for wind projects that are consistent with the
regulatory preservation standard at the LAP scale. The Service will use
all available information and the best available tools to estimate
where authorized take rates may be the highest relative to our
estimated eagle-population densities. Further, we will require Service-
approved in-lieu fee programs to allocate a small amount of
compensatory mitigation from each general permittee to be available to
address LAP concerns. With these extra mitigation funds, in-lieu fee
programs can deploy compensatory mitigation for eagles in areas where
LAP thresholds are close to being exceeded (or have been exceeded). If,
after expenditure of these funds, the Service still determines that
general-permit issuance is not consistent with the preservation
standard, we retain the right to amend, suspend, or revoke general
permits in order to safeguard local eagle populations.
Issue. We received comments regarding the take thresholds
associated with wind energy general permits, including comments that
such thresholds are not necessary for bald eagles, that such thresholds
may cause the general permit program to fail, and requests to remove
species-specific take thresholds.
Response. The Service calculated the take threshold for bald eagles
and the take threshold for golden eagles to ensure general permitting
is consistent with the preservation of both eagle species. The
calculated threshold for each species ended up being four eagles.
Ensuring take is compatible with eagle preservation primarily depends
on the take rates for each eagle species, not the combined take rate of
eagles in general. Therefore, there are separate take thresholds for
each species, not a combined threshold for ``eagles.'' Finding four
golden eagles creates a fatality estimate similar to what we would
expect to see at an average-sized project in the specific-permit zone.
Finding four bald eagles would produce a similar result. However, a
project that discovers two dead bald eagles and two dead golden eagles
during one permit term would be taking eagles at lower rates than
expected under specific permits and, thus, a general permit is
appropriate.
In response to comments that general permit take thresholds are not
necessary for bald eagles, we reiterate that the goal of these
thresholds is to ensure that the Service has appropriately accounted
for the level of eagle take for projects
[[Page 9941]]
receiving general permits in a way that is consistent with our
preservation standard and ensure that projects with relatively high
risk to eagles (of either species) are paired with the most appropriate
management actions that are commensurate with higher or uncertain take
rates. Exceeding the discovered eagles thresholds established by these
regulations is not a violation of the permit. Rather, a project that
discovers more than established thresholds indicates that there are
potentially unique circumstances at the project site that would benefit
from Service engagement through the specific permit process. The
specific permit process allows for Service review of site-specific data
and collaboration with the permit applicant on development of
additional data collection and avoidance and minimization approaches
appropriate for the project to ensure permit issuance criteria are met
and that authorized take is consistent with our preservation standard,
particularly at the local scale. This is not possible under an
automated general permit process.
In response to the comment that the general permit program is
likely to fail, our analysis of take in the general permit zones
suggests that it should be a rare wind project in the general permit
zone that takes eagles at rates high enough to discover four or more
bald eagles within a 5-year period. Our estimates for even large wind
projects in the general permit zone are substantially lower than
estimated bald eagle fatalities at a similar-sized project in the
specific permit zone, on which the four-eagle threshold was based.
Thus, we expect that only a small proportion of projects receiving
general permits will exceed the bald eagle threshold.
Issue. The Service received multiple comments regarding the use of
Evidence of Absence software (Dalthrop et al. 2017) for specific
permits; many of the comments requested that the Service eliminate the
use of Evidence of Absence software as a compliance measure. Instead of
Evidence of Absence software, one commenter suggested the Service
should instead assess compliance based on the actual number of eagles
found during fatality monitoring.
Response. The Service recognizes the limitations of Evidence of
Absence software. Therefore, on specific permits the Service will
authorize incidental take of bald eagles, golden eagles, or both but
will not specify a take limit. The Service will continue to use the
best available statistical programs to evaluate and estimate mortality
rates. Currently Evidence of Absence software is the best estimator
available to handle zero-inflated data (i.e., data that has an excess
of zero counts). The Service will use estimated mortality rates to
calculate compensatory mitigation requirements. The Service will also
use estimated mortality rates to estimate the number of eagles
authorized for internal tracking purposes. The Service will use
estimated mortality rates for eagles instead of number of eagles found,
as this approach is more appropriate for understanding how permit
issuance effects eagle populations.
Issue. Multiple comments expressed disapproval of the Collision
Risk Model (CRM), with some stating the lack of predictability with the
CRM results in increased costs and timelines.
Response. The Service recognizes that, as with all models, we must
continue working to improve the CRM. However, the CRM represents the
best science available today. The CRM was developed using site-specific
and species-specific eagle exposure and eagle collision data provided
from wind energy facilities across the Nation and represents the best
available data to assess risk to eagles by turbines. The Service's CRM
evaluates risk across projects in a consistent and predictable way
while accounting and managing for uncertainty. The Service uses site-
specific data to inform the CRM and have the estimate reflect risk for
a given project while accounting for variability in both eagle use and
collision risk. In the 2016 eagle rule and PEIS, the Service described
the adaptive management framework for authorization of eagle take. At
wind facilities, the Services uses monitoring data--consistent with
methods outlined in the Land-Based Wind Energy Guidelines (www.fws.gov/media/land-based-wind-energy-guidelines)--to inform the initial take
authorization for a permit. We use monitoring data collected under the
permit to update the estimates over time. Any mitigation paid by the
permittee initially that exceeds updated take estimates is credited
forward, reducing future mitigation burden.
The Service can evaluate alternative models as part of the adaptive
management framework over time; however, to ensure consistency and
adherence to management objectives, initial permit estimates are based
on our peer-reviewed modeling framework. Monitoring can be designed, in
coordination with the Service, to compare updates to the CRM modeling
framework to results from other models. Any comparison would need to
evaluate the model's ability to quantify uncertainty. Similarly, the
Service's eagle permit biologists consider all site-specific data
available when thinking about potential avoidance and minimization
measures that may reduce risk at a given project, but rely on the CRM
and consistent, representative monitoring data to represent risk across
all permitted projects. Site-specific data (e.g., mortality monitoring)
without use of a model designed to extrapolate beyond the monitoring
period does not appropriately account for variability in eagle risk.
The Service will use the CRM to calculate eagle fatalities for
internal tracking and calculating mitigation requirements for specific
permits. While the Service generally does not recommend that project
proponents propose an alternative CRM, under the new rule Tier 2
specific permittees with a reimbursable agreement may request
consideration of an alternative CRM. The Service will review these
requests on a case-by-case basis and anticipates requiring, at a
minimum, publication of the alternative CRM in the Federal Register for
public review at the cost of the applicant, including quantification of
the uncertainty of the model (i.e., confidence in the estimate). The
Service may also require third-party monitoring to validate the model.
Issue. Commenters requested clarification on take limits associated
with the permits.
Response. Wind energy general permits and specific permits will not
have a take limit associated with them. Wind projects with a general
permit cannot discover four or more bald eagles or four or more golden
eagles within a 5-year permit term and remain eligible for another
general permit in the future. We will continue to estimate take at wind
projects for both general and specific permits to ensure consistency
with the preservation standard and, for specific permits, determine
required compensatory mitigation. For specific permits, the Service
will require additional compensatory mitigation if it concludes
(through data received in annual reporting or otherwise) that permitted
take exceeds the level of compensatory mitigation already provided. If
we determine that take at a permitted facility is not consistent with
our preservation standard, we will conduct an administrative check-in
and likely require amendments to the permit.
[[Page 9942]]
Required Determinations
Regulatory Planning and Review (Executive Orders 12866, 13563, and
14094)
Executive Order 12866 (E.O. 12866), as reaffirmed by E.O. 13563 and
E.O. 14094, provides that the Office of Information and Regulatory
Affairs (OIRA) in the Office of Management and Budget (OMB) will review
all significant rules. OIRA has determined that this rulemaking action
is significant.
Executive Order 14094 reaffirms the principles of E.O. 12866 and
E.O 13563 and states that regulatory analysis should facilitate agency
efforts to develop regulations that serve the public interest, advance
statutory objectives, and are consistent with E.O. 12866, E.O. 13563,
and the Presidential Memorandum of January 20, 2021 (Modernizing
Regulatory Review). Regulatory analysis, as practicable and
appropriate, shall recognize distributive impacts and equity, to the
extent permitted by law. E.O. 13563 emphasizes further that regulations
must be based on the best available science and that the rulemaking
process must allow for public participation and an open exchange of
ideas. We have developed this rule in a manner consistent with these
requirements.
Costs and benefits of the rule can be broken down into three
categories; impacts to permittees, impacts to the Service, and societal
impacts. Impacts to permittees include permitting costs as described in
Table 1, below, as well as other unquantifiable costs such as the costs
associated with reading and understanding the rule, time spent on
permit application, and costs associated with training staff on the
requirements of the rule. Benefits to permittees include the ability to
acquire a permit and eliminate the risk of enforcement associated with
incidental eagle take. Where the costs of the proposed permit exceed
the benefits associated with the risk of enforcement (e.g., projects
with low risk of incidental eagle take or projects with perceived low
risk of legal enforcement), we do not expect entities to apply for a
permit. Impacts to the Service include costs associated with processing
and auditing these permits; these costs are anticipated to be less than
the benefits of anticipated reductions in staff time associated with
processing these permits, as general permits can be issued without the
need for Service interaction. Societal impacts include benefits
associated with an anticipated increase in eagle populations associated
with reduced incidental take and beneficial activities associated with
compensatory mitigation requirements; no societal costs are assumed.
Table 1 below shows the permit count and cost under the 2016
regulations, the expected number of permits and average permit costs
under this rule, and the estimated marginal costs and impacts between
the 2016 regulations and this rule. Additional analysis is available in
the supporting FEA.
BILLING CODE 4333-15-P
[[Page 9943]]
[GRAPHIC] [TIFF OMITTED] TR12FE24.010
[[Page 9944]]
[GRAPHIC] [TIFF OMITTED] TR12FE24.011
BILLING CODE 4333-15-C
The maximum total estimated annual cost to industry for this rule
is $16,821,500. The maximum total estimated cost over 5 years for all
permits is $84,107,500. The average annual equivalent cost is
$13,794,294 with a total net present value cost of $68,971,471 using a
7 percent discount rate. The average annual equivalent cost is
$15,407,509 with a total net present value of $77,037,544 at a 3
percent discount rate. These discount rates represent a range of values
that the Office of Management and Budget recommends as a Federal-
program discount rate for benefit-cost analysis for most Federal
programs. The above costs represent the total gross cost of the rule
and do not reflect the costs associated with the existing regulations.
This rule is expected to create an estimated maximum of $3,857,500 in
new costs annually and $19,287,500 in new marginal costs over 5 years,
as compared to the 2016 regulations. These estimates represent the
maximum quantifiable costs; they do not represent other costs that may
be incurred, such as the costs for entities to read and understand the
rule, time spent on permit application, and costs associated with
training staff on the requirements of the rule. However, these new
marginal costs are more than offset by savings to both industry and the
Service in terms of reduced Eagle Act enforcement costs and no
requirements for preconstruction monitoring under general permits and
the removed requirement for third-party monitoring under specific
permits. The anticipated 74 wind-energy projects and 4 power-line
entities that annually receive and comply with a permit will no longer
be subject to potential enforcement under
[[Page 9945]]
the Eagle Act, which can result in substantial legal costs, nor will
they incur costs to estimate and reduce their legal risks, which may
include biological surveys and hiring staff and attorneys. While this
total reduced enforcement cost is not quantifiable due to limited data,
the Service expects that the savings exceed the total new costs
associated with this rule. The costs of this rule are also offset by
the ecosystem-services benefits associated with potential decreased
take leading to increased populations of eagles.
Regulatory Flexibility Act (5 U.S.C. 601 et seq.)
Under the Regulatory Flexibility Act (5 U.S.C. 601 et seq., as
amended by the Small Business Regulatory Enforcement Fairness Act
(SBREFA) of 1996 (Pub. L. 104-121, 201, 110 Stat. 847)), whenever an
agency is required to publish a notice of rulemaking for any proposed
or final rule, it must prepare and make available for public comment a
regulatory flexibility analysis that describes the effect of the rule
on small businesses, small organizations, and small government
jurisdictions. However, no regulatory flexibility analysis is required
if the head of an agency certifies the rule would not have a
significant economic impact on a substantial number of small entities.
SBREFA amended the Regulatory Flexibility Act to require Federal
agencies to provide the statement of the factual basis for certifying
that a rule would not have a significant economic impact on a
substantial number of small entities. Thus, for a regulatory
flexibility analysis to be required, impacts must exceed a threshold
for ``significant impact'' and a threshold for a ``substantial number
of small entities.'' See 5 U.S.C. 605(b). We examined this rule's
potential effects on small entities as required by the Regulatory
Flexibility Act and certify that this action will not have a
significant economic impact on a substantial number of small entities.
This analysis first estimates the number of businesses potentially
impacted and then estimates the economic impact of this rule.
To assess the effects of this rule on small entities, we focus on
the proposed general and specific permit approach for incidental take
by wind-energy facilities and electric-transmission companies. We also
address nest disturbance and nest take permits for businesses in other
sectors, such as housing and building construction, railroads, timber
companies, pipeline companies, and gold ore mining.
Using the North American Industry Classification System (NAICS),
the U.S. Small Business Administration (SBA) defines a small business
as one with annual revenue or employment that meets or is below an
established size standard. While the NAICS was updated in 2023, we are
using the 2017 NAICS to best compare to the most recent 2017 Statistics
of U.S. Businesses (SUSB) tables that contain information on receipts.
Relevant 2017 NAICS small business definitions include:
[ballot] fewer than 250 employees for ``Wind Electric Power
Generation'' (NAICS sector 221115),
[ballot] fewer than 1,000 employees for ``Electric Power
Distribution'' (NAICS sector 221122),
[ballot] fewer than 500 employees for ``Logging'' (NAICS sector
113310),
[ballot] less than $36.5 million of average annual receipts for
``Construction of Buildings'' (NAICS sectors 236115, 236116, 236117,
236210, and 236220),
[ballot] less than $36.5 million of average annual receipts for
``Highway, Street, and Bridge Construction'' (NAICS sector 237310),
[ballot] less than $15.0 million of average annual receipts for
``Support Activities for Rail Transportation'' (NAICS sector 488210),
and
[ballot] fewer than 1,500 employees for ``Gold Ore Mining'' (NAICS
sector 212221).
Table 2 indicates the number of businesses within each industry and
the estimated percentage of small businesses impacted by this rule.
Table 2--Distribution and Potential Impact to Businesses \1\
----------------------------------------------------------------------------------------------------------------
Total firms/ Small businesses
establishments potentially impacted by
-------------------------- this rule
NAICS code Description Number of Number of -------------------------
all small
businesses businesses Number Percentage
----------------------------------------------------------------------------------------------------------------
221115...................... Wind Electric Power Generation 459 135 22 16
\2\.
221122...................... Electric Power Distribution 1,233 1,169 0 0
\3\.
113310...................... Logging \4\................... 7,992 7,977 up to 13 <1
236115...................... New Single-family Housing 49,215 49,143 up to 13 <1
Construction (Except For-Sale
Builders) \4\.
236116...................... New Multifamily Housing 3,175 2,851 up to 13 <1
Construction (Except For-Sale
Builders) \4\.
236117...................... New Housing For-Sale Builders 15,483 15,099 up to 13 <1
\4\.
236118...................... Residential Remodelers \4\.... 103,079 102,998 up to 13 <1
236210...................... Industrial Building 2,997 2,847 up to 13 1
Construction \4\.
236220...................... Commercial and Institutional 38,079 36,100 up to 13 <1
Building Construction \4\.
237310...................... Highway, Street, and Bridge 8,826 8,198 up to 13 <1
Construction \4\.
237990...................... Other Heavy and Civil 4,165 4,052 up to 13 <1
Engineering Construction \4\.
488210...................... Support Activities for Rail 564 484 up to 13 3
Transportation \4\.
212221...................... Gold Ore Mining \4\........... 147 132 up to 2 2
----------------------------------------------------------------------------------------------------------------
\1\ Data is from the latest Statistics of U.S. Businesses (SUSB) tables that contain information on receipts,
which is from 2017.
\2\ The number of potentially impacted small businesses is based on the distribution of businesses by enterprise
size from 2017 SUSB data tables, the total number of estimated annual permits, and the small business
standards threshold from SBA.
\3\ Permitting will be required at a large utility scale similar to existing Special Purpose Utility permits
(SPUT permits) that the Service issues.
\4\ We estimate that the number of nest disturbance and nest take permits will be similar to the number issued
over the last 5 years: 677. The non-electric and wind power generation NAICS represent sectors that have
historically requested permits. We evenly distributed the estimated total amount of disturbance and take
permits across all sectors, with the exception of gold ore mining, for the 5-year period, which comes to 67
permits. Gold ore mining entities have historically applied for only 1 to 2 permits per year, or up to 10 over
a 5-year period. We also assumed an evenly distributed number of permits across each year, 13, for the
remainder of the sectors.
[[Page 9946]]
In the last 5 years (2017 through 2022), the Service has issued 26
permits to wind-energy generation facilities and 677 specific permits
to other entities, which averages about 141 permits annually. For the
677 non-wind specific permits, most were issued to businesses and to
government agencies, and the remaining were issued to individuals. The
number of specific permits issued under this rule over the first 5
years may be higher or lower than the existing permit program under the
2016 regulations due to the creation of general permits and the
remaining complexity associated with specific permits. General permits
typically allow the regulated community to apply for and obtain a
permit more easily, particularly when projects are designed at the
outset to comply with general-permit eligibility criteria. Specific
permits are available to wind-energy-project applicants that do not
meet general-permit eligibility criteria. Based on these assumptions,
we estimate that the number of specific permits under this rule will be
similar to the number of existing permits over the last 5 years, which
is close to 30 permits. Although small, noncommercial, wind-energy
facilities (e.g., single-turbine facilities connected to public
buildings) could apply for incidental take permits, we anticipate that
most of the applications for wind-energy facilities will be for
utility-scale projects. The largest expected impacts to small
businesses under this rule would be an increase in the number of
permits issued to wind-energy generation facilities due to the changes
being made in the application requirements and the availability of
general permits and the inclusion of general and specific permits
tailored to power-line entities. We expect that this rule will impact
16 percent of wind-energy generation small businesses, with the
expected costs of such permits described in tables 3 (general permits)
and 4 (specific permits), and a breakdown of general permits by
enterprise size category in table 5.
Electric power distribution entities are eligible for both general
and specific incidental take permits in the proposed regulation.
However, based on the NAICS definitions, we assume that none of the
potential electric power distribution permittees would be small
businesses.
Businesses that apply for nest take and nest-disturbance permits
typically include home construction, road construction, and various
other construction projects. We assume that the number of nest take and
nest disturbance permits will continue along this trend over the next 5
years. For this analysis, we evenly distributed those permits across
industry sectors that best represent the NAICS industry sectors that
applied for permits historically. We anticipate the number of permit
applicants in those sectors would be relatively small, on the order of
1 to 13 per year for each sector, except gold ore mining, which
historically applied for only 1 to 2 permits annually. As a result,
this rule will impact less than 1 to 2.5 percent of small businesses in
NAICS sectors 236115, 236116, 236117, 236118, 236210, 236220, 237310,
237990, 488210, and 212221. The cost per entity for nest take and nest
disturbance permitting under this rule is minimal, totaling $100 per
eagle or nest, per year. The minimal cost of these permits is not
expected to result in a significant impact to small businesses in these
sectors, regardless of the total percentage of small businesses
impacted as a whole.
As described above, the wind-energy generation industry is the only
industry for which specific and general permits could result in a
significant impact on small businesses. Table 3 shows the expected
difference between 5-year costs for specific permits and 5-year costs
for general permits for wind-energy generation facilities. Wind-energy
generation facilities will pay less for a general permit compared to
the costs associated with a standard permit under the 2016 regulations.
The permit application fee (including costs for auditing) is reduced
from $36,000 to $1,000 for a general permit. In addition, applicants
will pay an administration fee of either $2,500 (Tier 1) or $10,000
(Tier 2), as compared to the existing specific permit administration
fee of $8,000. Compensatory mitigation costs for general permits for a
wind-energy project will average $37,200. This is a significant
decrease from the specific-permit cost under the 2016 regulations of
$960,000 (using our calculation from the EA of $120,000 as the cost of
an eagle credit). The average costs for monitoring for a wind-energy
project will be negligible, a cost savings from the specific permit
monitoring cost estimates of $1,100,000 under the 2016 regulations. The
total estimated cost savings between a specific permit under the 2016
regulations and a general permit under this regulation is therefore
slightly over $2,000,000 per permit (depending on whether the project
is a Tier 1 or a Tier 2 project). The total number of estimated permits
shows an estimated overall increase in industry costs associated with
permitting under this rule, but only because the Service expects a
substantial jump in participation across industry due to the
improvements in the permit process and reduction in costs and time
required per permit.
Table 3--Wind General Permit Costs and Savings
[5-Year costs]
----------------------------------------------------------------------------------------------------------------
Specific--2016
Cost category regulations General--this rule Cost savings (average)
(average) (average)
----------------------------------------------------------------------------------------------------------------
Permit application fee................. $36,000 $1,000.................... $35,000.
Administration Fee..................... 8,000 2,500 (Tier 1); 10,000 5,500 (Tier 1); (2,000)
(Tier 2). (Tier 2).
Compensatory Mitigation Costs.......... 960,000 37,200.................... 922,800.
Monitoring Costs....................... 1,100,000 0......................... 1,100,000.
------------------------------------------------------------------------
Total Cost......................... 2,104,000 40,700 (Tier 1); 48,200 2,063,300 (Tier 1);
(Tier 2). 2,055,800 (Tier 2).
----------------------------------------------------------------------------------------------------------------
Table 4 displays the new cost for specific permits under this rule
compared to the cost for specific permits under the 2016 regulations.
Under this rule, entities will pay $1,080,000 for compensatory
mitigation, an increase of $120,000 from the $960,000 cost under the
2016 regulations. These costs have increased due to updates in the
estimated amount of required mitigation for projects in the specific-
permit category. The Service may issue three types of wind-energy
specific permits under this rule. Tier 1 permits are for the simplest
types of
[[Page 9947]]
projects and would require a $10,000 permit-application cost. Tier 2
permits are similar to existing specific permits and require a $26,000
permit application cost. Tier 2 with reimbursable agreement permits
require permittees to pay for staff time via a reimbursable agreement
above and beyond the $26,000 permit application cost. For purposes of
this analysis, we assume that the average specific permit will be a
Tier 2 permit with the same permit-application cost as the specific-
permit structure under the 2016 regulations. Entities will continue to
pay their own monitoring costs estimated at $1,100,000 over the life of
the permit. As a result, the total average cost increase to entities
receiving a wind-energy specific permit under this rule is $112,000.
Table 4--Wind Energy Specific Permit Costs and Savings
[5-Year costs]
----------------------------------------------------------------------------------------------------------------
Specific--2016 Specific--
Cost category regulations this rule Cost savings
(average) (average) (average)
----------------------------------------------------------------------------------------------------------------
Permit Application Fee........................................ $36,000 $26,000 $10,000
Administration Fee............................................ 8,000 10,000 (2,000)
Compensatory Mitigation Costs................................. 960,000 1,080,000 (120,000)
Monitoring Costs.............................................. 1,100,000 1,100,000 0
-------------------------------------------------
Total Cost................................................ 2,104,000 2,216,000 (112,000)
----------------------------------------------------------------------------------------------------------------
Businesses in the ``wind electric power generation industry'' are
defined as small if they have fewer than 250 employees. The 2017 SUSB
Annual Data Tables report the annual payroll amounts by industry that
fall within enterprise size categories. The data for ``wind electric
power generation'' does not contain a range for businesses with under
250 employees; the closest reporting range is fewer than 500 employees.
Table 5 shows a range of receipts by enterprise size and establishment
count as well as the projected percentage of receipts impacted by this
rule both at the individual establishments level and the total for that
enterprise size. The wind-energy project general-permit cost will be
paid in full at the time of the permit application; therefore, the 5-
year cost of $48,200 is assessed in the first year. This cost would
then be assessed again at the renewal of the permit in 5 years. Due to
this being a one-time cost that covers a 5-year period, this amount
equates to at most one percent of total annual receipts by enterprise
size (table 5). As a result, this cost will not create a substantial
impact on small businesses or specific industries. We base this
determination on permit costs for general permits. The number of
specific permits issued is expected to follow the same trend as under
the 2016 regulations, and permits are likely to be issued in areas of
higher risk to eagles to large, complex facilities that are well above
the industry-standard payroll amount. Therefore, we do not expect any
impacts to small businesses associated with these specific permits.
Table 5--Range of Receipts Impacted by This Rule: Wind Electric Power Generation General Permits
[Using 2017 SUSB annual data table]
--------------------------------------------------------------------------------------------------------------------------------------------------------
Average receipt
Annual for size Annual cost per Number of Total annual % Annual % of
Enterprise size \1\ Establishments receipts (=receipt/ permit for establishments of receipts receipts for
($1,000) establishments) establishment impacted impacted by impacted
($1,000) annually \2\ this rule establishments
--------------------------------------------------------------------------------------------------------------------------------------------------------
01: Total......................... 459 $8,001,761 $17,433 $48,200 74 0.04 0.3
02: <5 employees.................. 45 80,905 1,798 48,200 7 0.42 2.7
03: 5-9 employees................. 8 14,478 1,810 48,200 1 0.33 2.7
04: 10-14 employees............... 7 15,873 2,268 48,200 1 0.30 2.1
05: 15-19 employees............... 8 39,960 4,995 48,200 1 0.12 1.0
06: <20 employees................. 68 151,216 2,224 48,200 11 0.35 2.2
12: 50-74 employees............... 9 98,897 10,989 48,200 1 0.05 0.4
19: <500 employees................ 135 1,469,292 10,884 48,200 22 0.07 0.4
24: 2,000-2,499 employees......... 12 75,879 6,323 48,200 2 0.13 0.8
25: 2,500-4,999 employees......... 11 91,973 8,361 48,200 2 0.10 0.6
26: 5,000+ employees.............. 240 5,368,670 22,369 48,200 39 0.04 0.2
--------------------------------------------------------------------------------------------------------------------------------------------------------
\1\ 2017 NAICS thresholds for ``Wind Electric Power Generation'' (NAICS 221115) define small businesses as having fewer than 250 employees.
\2\ The number of establishments impacted annually is based on the weighting of the number of establishments in that enterprise size compared to the
total number of establishments. That weight value was multiplied by the total number of estimated annual permits (74) to derive the figures shown.
Note that the total sum of <500 and the enterprise sizes greater than 500 will not total 74 due to missing enterprise size categories from the SUSB
2017 data tables.
While electric-power-distribution companies are currently eligible
to apply for a specific permit, under this rule, these entities are
eligible to apply for general permits. The permit application fee for
these general permits is $1,000, and the administration fee is either
$2,500 (for Tier 1 permittees) or $10,000 (for Tier 2 permittees). The
costs for power-pole retrofits called for under the proactive retrofit
strategy are estimated to be $0. Many larger utilities already have
existing avian protection and retrofit strategies in place and would
not incur new costs or benefits associated with the proposed retrofit
strategy. For entities without an avian protection plan and a retrofit
strategy in place, we expect that the retrofit requirement for a
general permit will not create substantial new costs for those
entities. Any costs associated with retrofitting power poles to be
avian-safe (estimated from approximately $500-$2,500 per pole) would be
at least partly recouped by increased reliability and a reduction in
costs associated with eagle-
[[Page 9948]]
electrocution response. The Service assumes that the primary interest
in permits in the first 5 years would be from firms with existing
special-purpose-utility permits to salvage dead birds. These firms with
known incidental take of eagles will benefit from a permit authorizing
that take. No existing special-purpose-utility permit holder is a small
business, and, therefore, there will not be a substantial impact to
small businesses from this rule.
A commercial business applying for a standard nest disturbance or
nest take permit under the 2016 regulations would have to pay $500 per
nest per year, while a noncommercial entity would pay $100 per nest per
year. Under this rule, both commercial and noncommercial permittees
would pay $100 per nest per year for a general permit. Businesses in
the construction industry are defined as small if they have annual
revenue less than $36.5 million. Depending on the type of permit
applications submitted by an individual small business, the permit fees
represent less than one percent of revenue. Thus, the creation of a
general permit will not have a significant economic effect on a
substantial number of small businesses in the construction sectors. The
changes in general permit application fees are shown in tables 6 and 7.
The costs of a specific permit for both nest disturbance and nest take
would be unchanged from the existing regulation.
Table 6 shows the expected difference between the 5-year costs for
a nest-disturbance permit under the 2016 regulations and a general
permit under this rule.
Table 6--Nest Disturbance General Permit Costs and Savings
[5-Year costs]
----------------------------------------------------------------------------------------------------------------
Nest disturbance-- Nest disturbance--
Cost category 2016 regulations this rule Cost savings
----------------------------------------------------------------------------------------------------------------
Permit application costs......................... $2,500 $500 $2,000
----------------------------------------------------------------------------------------------------------------
Table 7 shows the expected difference between the 5-year costs for
a nest-take permit under the 2016 regulations and a general permit
under this rule.
Table 7--Nest Take General Permit Costs and Savings
[5-Year costs]
----------------------------------------------------------------------------------------------------------------
Nest take-- 2016
Cost category regulations Nest take-- this rule Cost savings
----------------------------------------------------------------------------------------------------------------
Permit Application Costs......................... $2,500 $500 $2,000
----------------------------------------------------------------------------------------------------------------
This rule is expected to create an overall savings due to reduced
costs for general permits compared to specific permits under the 2016
regulations. This rule is expected to create additional savings to both
industry and the Service in terms of reduced Eagle Act enforcement
costs. Entities that receive and comply with a permit will no longer be
subject to potential enforcement under the Eagle Act, which can result
in substantial legal costs, nor will they incur costs to estimate and
reduce their legal risks, which may include biological surveys and
hiring staff and attorneys. While this total reduced enforcement cost
is not quantifiable due to limited data, the Service expects that it
exceeds the total of new costs associated with this rule.
In sum, this rule impacts a substantial number of small businesses
in NAICS sector 221115, ``Wind Electric Power Generation''; however,
the economic impacts to individual businesses are not significant. As
described above, the number of businesses belonging to other industries
impacted is not substantial and the magnitude of those economic impacts
is not significant. Based on the available information analyzed above,
we certify that this rule will not have a significant economic effect
on a substantial number of small entities as defined under the
Regulatory Flexibility Act (5 U.S.C. 601 et seq.). Therefore, a
regulatory flexibility analysis is not required, and a small entity
compliance guide is not required.
Unfunded Mandates Reform Act (2 U.S.C. 1501 et seq.)
In accordance with the Unfunded Mandates Reform Act, we have
determined the following:
a. This rule will not ``significantly or uniquely'' affect small
governments in a negative way. There would be no permit administration
costs incurred by small governments because they would not be
administering the issuance of Federal permits. Small governments could
potentially apply for permits for nest take or nest disturbance, but
fees for those permits are small and would not significantly affect
small governments in a negative way. A small government agency plan is
not required.
b. This rule will not produce a Federal mandate of $100 million or
greater in any year. It is not a ``significant regulatory action''
under the Unfunded Mandates Reform Act.
Takings (E.O. 12630)
In accordance with E.O. 12630, this rule will not have significant
takings implications. This rule does not contain any provisions that
could constitute taking of private property. Therefore, a takings
implication assessment is not required.
Federalism (E.O. 13132)
This rule will not have sufficient federalism effects to warrant
preparation of a federalism summary impact statement under E.O. 13132.
It will not interfere with the States' abilities to manage themselves
or their funds. No significant economic impacts are expected to result
from the regulations changes.
Civil Justice Reform (E.O. 12988)
In accordance with E.O. 12988, the Office of the Solicitor has
determined that this rule does not unduly burden the judicial system
and meets the requirements of sections 3(a) and 3(b)(2) of the Order.
Paperwork Reduction Act (44 U.S.C. 3501 et seq.)
This rule contains existing and new information collections. All
information
[[Page 9949]]
collections require approval by the Office of Management and Budget
(OMB) under the Paperwork Reduction Act of 1995 (PRA, 44 U.S.C. 3501 et
seq.). We may not conduct or sponsor, and you are not required to
respond to, a collection of information unless it displays a currently
valid OMB control number. The OMB has reviewed and approved the
information collection requirements associated with eagle permits and
fees and assigned the OMB Control Number 1018-0167.
In accordance with the PRA and its implementing regulations at 5
CFR 1320.8(d)(1), we provide the general public and other Federal
agencies with an opportunity to comment on our proposal to revise OMB
Control Number 1018-0167. This input will help us assess the impact of
our information collection requirements and minimize the public's
reporting burden. It will also help the public understand our
information collection requirements and provide the requested data in
the desired format.
As part of our continuing effort to reduce paperwork and respondent
burdens, and in accordance with 5 CFR 1320.8(d)(1), we invite the
public and other Federal agencies to comment on any aspect of this
proposed information collection, including:
(1) Whether or not the collection of information is necessary for
the proper performance of the functions of the agency, including
whether or not the information will have practical utility;
(2) The accuracy of our estimate of the burden for this collection
of information, including the validity of the methodology and
assumptions used;
(3) Ways to enhance the quality, utility, and clarity of the
information to be collected; and
(4) Ways to minimize the burden of the collection of information on
those who are to respond, including through the use of appropriate
automated, electronic, mechanical, or other technological collection
techniques or other forms of information technology, e.g., permitting
electronic submission of response.
Comments that you submit in response to this rulemaking are a
matter of public record. Before including your address, phone number,
email address, or other personal identifying information in your
comment, you should be aware that your entire comment--including your
personal identifying information--may be made publicly available at any
time. While you can ask us in your comment to withhold your personal
identifying information from public review, we cannot guarantee that we
will be able to do so.
The Bald and Golden Eagle Protection Act (Eagle Act; 16 U.S.C. 668-
668d) prohibits take of bald eagles and golden eagles except pursuant
to Federal regulations. The Eagle Act regulations at title 50, part 22
of the CFR define the ``take'' of an eagle to include the following
broad range of actions: To ``pursue, shoot, shoot at, poison, wound,
kill, capture, trap, collect, destroy, molest, or disturb.'' The Eagle
Act allows the Secretary of the Interior to authorize certain otherwise
prohibited activities through regulations. Service permit applications
associated with eagles are each tailored to a specific activity based
on the requirements for specific types of permits. We collect standard
identifier information for all permits. The information that we collect
on applications and reports is the minimum necessary for us to
determine if the applicant meets/continues to meet issuance
requirements for the particular activity. Standardizing general
information common to the application forms makes filing of
applications easier for the public as well as expedites our review of
applications. In accordance with Federal regulations at 50 CFR 13.12,
we collect standard identifier information for all permits, including
the following:
Applicant's full name and address (street address, city,
county, State, and zip code; and mailing address if different from
street address); home and work telephone numbers; and a fax number and
email address (if available), and
--If the applicant resides or is located outside the United States, an
address in the United States, and, if conducting commercial activities,
the name and address of his or her agent that is located in the United
States; and
--If the applicant is an individual, the date of birth, occupation, and
any business, agency, organizational, or institutional affiliation
associated with the wildlife or plants to be covered by the license or
permit; or
--If the applicant is a business, corporation, public agency, or
institution, the tax identification number; description of the business
type, corporation, agency, or institution; and the name and title of
the person responsible for the permit (e.g., president, principal
officer, or director);
Location where the requested permitted activity is to
occur;
Reference to the part(s) and section(s) of subchapter B as
listed in 50 CFR 13.11(b) under which the application is made for a
permit or permits, together with any additional justification,
including supporting documentation as required by the referenced
part(s) and section(s);
If the requested permitted activity involves the import or
reexport of wildlife or plants from or to any foreign country, and the
country of origin, or the country of export or re-export restricts the
taking, possession, transportation, exportation, or sale of wildlife or
plants, documentation as indicated in 50 CFR 14.52(c);
Certification containing the following language:
--I hereby certify that I have read and am familiar with the
regulations contained in title 50, part 13, of the Code of Federal
Regulations and the other applicable parts in subchapter B of chapter I
of title 50, Code of Federal Regulations, and I further certify that
the information submitted in this application for a permit is complete
and accurate to the best of my knowledge and belief. I understand that
any false statement herein may subject me to suspension or revocation
of this permit and to the criminal penalties of 18 U.S.C. 1001.
Desired effective date of permit (except where issuance
date is fixed by the part under which the permit is issued);
Date;
Signature of the applicant; and
Other information that the Director determines relevant to
the processing of the application, including, but not limited to,
information on the environmental effects of the activity consistent
with 40 CFR 1506.5 and Departmental procedures at 516 DM 8.
In addition to the general permitting requirements outlined in
Federal regulations at 50 CFR 13.12, applications for any permit under
50 CFR part 22 must contain:
Species of eagle and number of birds, nests, or eggs
proposed to be taken, possessed, or transported;
Specific locality in which taking is proposed, if any;
Method of proposed take, if any;
If not taken, the source of eagles and other circumstances
surrounding the proposed acquisition or transportation;
Name and address of the public museum, public scientific
society, or public zoological park for which they are intended; and
Complete explanation and justification of the request,
nature of project or study, number of specimens now at the institution,
reason these are
[[Page 9950]]
inadequate, and other appropriate explanations.
The proposed revisions to existing and new reporting and/or
recordkeeping requirements identified below require approval by OMB:
(1) Administrative Updates--On January 7, 2022, the Service
published a final rule (87 FR 876) making administrative updates to 50
CFR parts 21 and 22. We captured the associated administrative updates
to the CFR references for part 22 in the updated versions of the forms
in this collection being submitted to OMB for approval with this
renewal/revision request.
(2) Change in Administration Fees--State, Local, Tribal, or Federal
Agencies (Sec. 13.11(d)(3)(i))--This rule changes the Service's
practice of not charging administration fees for eagle permits under 50
CFR part 22 to any State, local, Tribal, or Federal government agency,
or to any individual or institution acting on behalf of the agency.
Except as otherwise authorized or waived, if the agency fails to submit
evidence of agency status with the application, we will require the
submission of all processing fees prior to the acceptance of the
application for processing.
(3) Revision to Form 3-200-71--We split approved Form 3-200-71,
``Eagle Take Associated with but not the Purpose of an Activity
(Incidental Take)'' into two separate forms * as follows:
a. Form 3-200-71, ``Eagle Incidental Take''--General and Specific,
and
b. Form 3-200-91, ``Eagle Disturbance Take''--General and Specific.
* With this submission, we are no longer proposing Form 3-200-
92, Eagle Incidental Take (Power Lines)--General and Specific.''
We further describe the changes below:
a. (Revised Title) Form 3-200-71, ``Eagle Incidental Take''--
General and Specific--The revision to Form 3-200-71 authorizes the
incidental take of eagles where the take results from but is not the
purpose of an activity. General permits are valid for 5 years from the
date of registration. Specific permits may be valid for up to 30 years.
In addition to the standardized information required by 50 CFR 13.12,
permit application requirements include submission of the following
information:
i. Requested permit type;
ii. Infrastructure type;
iii. Description, duration, and location of the activity that is
likely to cause eagle take;
iv. Justification of why there is no practicable alternative to the
activity that would protect the interest to be served;
v. Description of eagle use and activity in the area, location of
eagle nests or roosts, and distance of nests and other important eagle
use areas from the project;
vi. Identification of subpermittees, if applicable;
vii. Records retention requirements;
viii. Certification of activity's compliance with all Federal,
Tribal, State, and local laws and regulations applicable to eagles; and
ix. Permit disqualification factors, including information for any
convictions, guilty pleas or nolo contendere, forfeited collateral, or
pending charges for violations of laws cited in the permit application.
General permit applications must also include the compensatory
mitigation requirement, requested permit tenure and effective date, and
certification of general permit requirements. Additional information
collected from specific permit applicants includes:
i. Requested duration of the permit;
ii. Requested eagle species for authorization;
iii. Additional project-specific information, including an eagle
impacts assessment and pre- or post-construction monitoring methods;
iv. Description of implemented and proposed avoidance and
minimization measures;
v. Description of implemented and proposed compensatory mitigation;
vi. Existing project general permit eligibility, if applicable; and
vii. Anticipated permit application fee tier.
Permit applications associated with eagle incidental take permits
may require the following:
Post-Construction Monitoring--Post-construction monitoring
fatality estimation must be based on 2 or more years of eagle fatality
monitoring that meet the Service's minimum fatality monitoring
requirements for specific eagle permits.
Adaptive Management Plan--Upon the discovery of the third
and fourth bald eagle or golden eagle injuries or mortalities at a
project, the permittee must provide the Service with their reporting
data required by the permit conditions, adaptive management plan, and a
description and justification of which adaptive management approaches
will be implemented.
Annual Report--Permittees must submit an annual report
using Form 3-202-15. The annual report is due within 30 days of the
expiration of the permit or prior to requesting renewal of the permit,
whichever is first.
Compensatory Mitigation--For wind energy specific permits,
the permittee must implement the compensatory mitigation requirements
on the face of their permit. For wind energy general permits, the
permittee must obtain eagle credits from a Service-approved
conservation bank or in-lieu fee program based on the hazardous volume
of the project.
In addition, permit applications associated with incidental take
permits by power lines may require the following:
Collision Response Strategy--A plan that describes the
process the permittee will follow to identify whether a collision-
caused injury or morality has occurred, to evaluate factors that
contributed to the collision, and to implement risk-reduction measures
commensurate with the collision risk.
Proactive Retrofit Strategy--A plan to convert existing
infrastructure to avian-safe infrastructure within a set timeline. The
strategy must identify a baseline of poles to be proactively retrofit.
The existing-infrastructure baseline must include all poles that are
not avian-safe for eagles located in areas identified by the applicant
to be high risk to eagles and may also include other poles in the
service area.
Reactive Retrofit Strategy--A plan to respond to incidents
where eagles are electrocuted or killed. The reactive retrofit strategy
must include information on how eagle electrocutions are detected and
identified. Determining which poles to retrofit must be based on the
risk to eagles and not on other factors (e.g., convenience or cost).
The pole that caused the electrocution must be retrofitted unless the
pole is already avian-safe. A total of 13 poles or a half-mile segment
must be retrofitted, whichever is less, prioritizing the highest risk
poles closest to the electrocution event.
Shooting Response Strategy--A plan that describes the
process the permittee will follow when eagles are found killed or
injured near power-line infrastructure to identify if shooting is
suspected, to communicate with law enforcement, and to identify and
implement appropriate shooting reduction measures.
The Service will use the information collected via the form to
track whether the take level is exceeded or is likely to be exceeded,
to determine that the take is necessary, and that the take will be
compatible with the preservation of eagles.
b. (NEW) Form 3-200-91, ``Eagle Disturbance Take''--General and
Specific--Applicants may apply for an eagle disturbance take permit if
their activity may result in incidental
[[Page 9951]]
disturbance of bald eagles or golden eagles. General permits issued
under this section are available only for certain activities that cause
disturbance of bald eagles and are valid for a maximum of 1 year.
General permits are not available for disturbance of nests located in
Indian country (18 U.S.C. 1151), unless the Tribe is the applicant.
Specific permits are intended for disturbance of a golden eagle nest,
disturbance of a bald eagle nest by an activity not specified in
paragraph (b) of Sec. 22.280, or disturbance of eagles caused by
physical or functional elimination of all foraging area within a
territory. The tenure of specific permits is set forth on the face of
the permit and may not exceed 5 years. In addition to the standardized
information required by 50 CFR 13.12, permit application requirements
include submission of the following information:
i. Requested permit type;
ii. Description, duration, and location of the activity that is
likely to cause disturbance to eagles;
iii. Justification of why there is no practicable alternative to
the activity that would protect the interest to be served;
iv. Description of eagle use and activity in the area, location of
eagle nests or roosts, and distance of nests and other important eagle
use areas from the project;
v. Identification of subpermittees, if applicable;
vi. Records retention requirements;
vii. Certification of activity's compliance with all Federal,
Tribal, State, and local laws and regulations applicable to eagles; and
viii. Permit disqualification factors, including information for
any convictions, guilty pleas or nolo contendere, forfeited collateral,
or pending charges for violations of laws cited in the permit
application.
General permit applications must also include the requested permit
tenure and effective date and certification of general permit
requirements. Additional information collected from specific permit
applicants includes:
i. Organization status (e.g., commercial or non-commercial);
ii. Requested duration of the permit;
iii. Assessment of impacts to eagles;
iv. Description of implemented and proposed avoidance and
minimization measures;
v. Description of implemented and proposed compensatory mitigation
for golden eagle nest disturbance, if applicable; and
vi. Description of efforts to monitor for impacts to eagles.
Permit applications associated with eagle disturbance take may
require the following:
Monitoring--The permittee must monitor the nest to
determine whether nestlings have fledged from the nest. We updated the
burden for monitoring requirements associated with disturbance take in
the separate monitoring information collection requirement.
Annual Report--Permittees must submit an annual report
using Form 3-202-15. The annual report is due within 30 days of the
expiration of the permit or prior to requesting renewal of the permit,
whichever is first.
The Service will use the information collected via the form to
track whether the take level is exceeded or is likely to be exceeded,
to determine that the take is necessary, and that the take will be
compatible with the preservation of eagles.
(4) Revision to Form 3-200-72--We are revising Form 3-200-72,
``Eagle Nest Take'' as described below:
Form 3-200-72 is used to apply for authorized take of bald eagle
nests or golden eagle nests, including relocation, removal, and
otherwise temporarily or permanently preventing eagles from using the
nest structure for breeding under definitions in 50 CFR 22.300(b).
General permits are available for bald eagle nest take for emergency,
nest take for health and safety, or nest take for a human-engineered
structure, or, if located in Alaska, other purposes. General permits
may authorize bald eagle nest removal from the nesting substrate at the
location requested and the location of any subsequent nesting attempts
by the eagle pair within one-half mile of the location requested for
the duration of the permit. Take of an additional eagle nest(s) more
than one-half mile away requires additional permit(s). General permits
are valid until the start of the next breeding season, not to exceed 1
year. General permits are not available for take of nests located in
Indian country (18 U.S.C. 1151), unless the Tribe is the applicant.
Specific permits are required for take of a golden eagle nest for any
purpose, take for species protection, and, except for Alaska, nest take
for other purposes. The tenure of specific permits is set forth on the
face of the permit and may not exceed 5 years.
In addition to the standardized information required by 50 CFR
13.12, permit application requirements include submission of the
following information:
a. Requested permit type;
b. Description and location of the activity that will result in
eagle nest take;
c. Selected purpose of nest take;
d. Justification of why there is no practicable alternative to the
activity that would protect the interest to be served;
e. Description of the nest(s), including species, location, and
historic and current nest status;
f. Description of nest removal, destruction, or relocation,
including information related to re-nesting and donation of eagle nests
and parts.
g. Identification of subpermittees, if applicable;
h. Records retention requirements;
i. Certification of activity's compliance with all Federal, Tribal,
State, and local laws and regulations applicable to eagles; and
j. Permit disqualification factors, including information for any
convictions, guilty pleas or nolo contendere, forfeited collateral, or
pending charges for violations of laws cited in the permit application.
General permit applications must also include the requested permit
tenure and effective date and certification of general permit
requirements. Additional information collected from specific permit
applicants includes:
i. Organization status (e.g., commercial or non-commercial);
ii. Requested duration of the permit;
iii. Assessment of impacts to eagles;
iv. Description of implemented and proposed avoidance and
minimization measures;
v. Description of implemented and proposed compensatory mitigation
for golden eagle nest take, if applicable;
vi. Description of efforts to monitor for impacts to eagles; and
vii. Description of method for removing nestlings or eggs and
proposed disposition, if applicable.
Permit applications associated with eagle nest take may require the
following:
Monitoring--Permittees must remove chicks or eggs from an
in-use nest for immediate transport to a foster nest, rehabilitation
facility, or as otherwise directed by the Service. If nestlings or eggs
are relocated with a nest or to a foster nest, the permittee must
monitor the nest to ensure adults are tending to nestlings or eggs. We
updated the burden for monitoring requirements associated with eagle
nest take in the separate monitoring information collection
requirement.
Annual Report--Permittees must submit an annual report
using Form 3-202-16. The annual report is due within 30 days of the
expiration of the permit
[[Page 9952]]
or prior to requesting renewal of the permit, whichever is first.
Species Protection--If a Federal, State, or Tribal agency
applies for a nest take permit for species protection, they must
provide documentation that describes relevant management efforts to
protect the species of concern; identifies and describes how the
nesting eagles are a limiting factor to recovery of the species using
the best available scientific information and data; and explains how
take of eagle nests is likely to have a positive effect on recovery for
the species of concern.
The Service will use the information collected via the form to
track whether the take level is exceeded or is likely to be exceeded,
to determine whether the take is necessary, and whether the take will
be compatible with the preservation of eagles.
(5) Permit Reviews--The Service removed the regulatory requirement
for specific permits to mandate an administrative check-in with the
Service at least every 5 years during the permit tenure. The Service
introduced these mandatory 5-year permit reviews as part of the 2016
Eagle Rule to ensure that the Service had an opportunity to ask for and
review all existing data related to a long-term activity's impacts on
eagles. The purpose of 5-year review is to update take estimates and
related compensatory mitigation for the subsequent 5-year period. It
also provides the Service with an opportunity to amend the permit to
reduce or eliminate conservation measures or other permit conditions
that prove to be ineffective or unnecessary. The purpose of these
reviews does not change with this rulemaking. However, the 5-year
requirement has introduced unintended uncertainty which, according to
public comment, has reduced participation in eagle take permitting
under the 2016 regulations. It has also resulted in timing issues,
where post-construction monitoring or other data is available off-cycle
from the 5-year timing (e.g., year 3 or 4) but cannot be used until the
scheduled check-in. Instead, check-ins may now be initiated by the
permittee or the Service in response to events that warrant review, for
example, updating fatality estimates and associated compensatory
mitigation requirements or revising permit conditions to reflect the
best available science.
(6) Reporting Requirements--Submission of reports is generally on
an annual basis, although some are dependent on specific transactions.
Additional monitoring and report requirements exist for permits issued
under 50 CFR part 22. Permittees must submit an annual report for every
year the permit is valid and for up to 3 years after the activity is
completed.
a. (New Reporting Requirement) Report Take of Eagles (3rd and 4th
Eagles) (50 CFR 22.250(d)(2) and (d)(3))--Permittees must notify the
Service in writing within 2 weeks of discovering the take of a third or
fourth bald eagle or a third or fourth golden eagle. The notification
must include the reporting data required in their permit conditions,
their adaptive management plan, and a description and justification of
which adaptive management approaches they will be implementing. Upon
notification of the take of the fourth bald eagle or fourth golden
eagle, the project will remain authorized to incidentally take eagles
through the term of the existing general permit but will not be
eligible for future general permits.
(7) (NEW) Audits--The Service will conduct audits of general
permits to ensure permittees are appropriately interpreting and
applying eligibility criteria and complying with permit conditions.
Audits may include reviewing application materials for completeness and
general permit eligibility. Any required records, plans, or other
documents will be requested of the permittee and reviewed. If there is
a compliance concern, the applicant will be given the opportunity to
submit additional information to address the concern. If, during an
audit, the Service determines that the permittee is not eligible for a
general permit or is out of compliance with general permit conditions,
we will communicate to the permittee options for coming into
compliance.
(8) (NEW--Existing In Use Without OMB Approval) Labeling
Requirement--Regulations at 50 CFR 22.4 require all shipments
containing bald or golden eagles, alive or dead, their parts, nests, or
eggs to be labeled. The shipments must be labeled with the name and
address of the person the shipment is going to, the name and address of
the person the shipment is coming from, an accurate list of contents by
species, and the name of each species.
(9) (NEW--Existing In Use Without OMB Approval) Requests for
Reconsideration Associated with Eagle Permits (Suspension and
Revocation)--Persons notified of the Service's intention to suspend or
revoke their permit may request reconsideration by complying with the
following:
Within 45 calendar days of the date of notification,
submit their request for reconsideration to the issuing officer in
writing, signed by the person requesting reconsideration or by the
legal representative of that person.
The request for reconsideration must state the decision
for which reconsideration is being requested and shall state the
reason(s) for the reconsideration, including presenting any new
information or facts pertinent to the issue(s) raised by the request
for reconsideration.
The request for reconsideration must contain a
certification in substantially the same form as that provided by 50 CFR
13.12(a)(5). If a request for reconsideration does not contain that
certification, but is otherwise timely and appropriate, the Service
will hold the request and give the person submitting the request
written notice of the need to submit the certification within 15
calendar days. Failure to submit certification will result in the
Service rejecting the request as insufficient in form and content.
(10) (NEW--Existing In Use Without OMB Approval) Compensatory
Mitigation (Sec. 22.220)--Any permit authorizing take that would
exceed the applicable EMU take limit will require compensatory
mitigation, except in circumstances where the action is considered in
the best interest of an eagle. Compensatory mitigation for this purpose
must ensure the preservation of the affected eagle species by
mitigating an amount equal to or greater than the authorized or
expected take. Compensatory mitigation must either reduce another
ongoing form of mortality or increase the eagle population of the
affected species. Compensatory mitigation for golden eagles must be
performed at a 1.2:1 (mitigation: take) ratio. A permit may require
compensatory mitigation when the Service determines, according to the
best available information, that the take authorized by the permitted
activity is not consistent with maintaining the persistence of the
local area population of an eagle species.
The Service must approve types of compensatory mitigation and may
include conservation banks, in-lieu fee programs, or permittee-
responsible mitigation as mitigation providers. General permittees meet
this requirement by obtaining required credits from a Service-approved,
third-party mitigation provider. Specific permittees can meet this
requirement by obtaining required credits from a Service-approved,
third-party mitigation provider or meeting the requirements to be a
permittee-responsible mitigation provider as described in 50 CFR
22.220(c)(2). Third-party mitigation providers, such as in-lieu fee
programs
[[Page 9953]]
and conservation banks, obtain Service approval by meeting the
requirements to be a mitigation provider as described in 50 CFR
22.220(c)(2).
To obtain approval as a mitigation provider, potential providers
must submit a mitigation plan to the Service that demonstrates how the
standards in 50 CFR 22.220(b) will be met. At a minimum, this must
include a description of the mitigation, the benefit to eagles, the
locations where projects will be implemented, the EMU and local area
population affected, the number of credits provided, and an explanation
of the rationale for the number of eagle credits provided. The Service
must approve the mitigation plan prior to implementation.
(11) (NEW--Existing In Use Without OMB Approval) Single Application
for Multiple Activities (50 CFR 13.11(d)(1))--If regulations require
more than one type of permit for an activity and permits are issued by
the same office, the issuing office may issue one consolidated permit.
Applicants may submit a single application in these cases, provided the
single application contains all the information required by the
separate applications for each permitted activity. In instances where
the Service consolidates more than one permitted activity into one
permit, the issuing office will charge the highest single fee for the
activity permitted. Administration fees are not waived for single
applications covering multiple activities.
We have renewed the existing reporting and recordkeeping
requirements identified below:
(1) Form 3-200-14, ``Eagle Exhibition''--This form is used to apply
for a permit to possess and use eagles and eagle specimens for
educational purposes. In addition to the standardized information
required by 50 CFR 13.12, permit application requirements include
submission of the following information: type of eagle(s) or eagle
specimens; status of other required authorizations (State, Tribal,
local); description of the programs that will be offered and how the
eagles will be displayed; experience of handlers; and information about
enclosures, diet, and enrichment for the eagles. The Service uses the
information collected via the form to determine whether the eagles are
legally acquired and will be used for bona fide conservation education,
and in the case of live eagles, will be housed and handled under safe
and healthy conditions.
(2) Form 3-200-15a, ``Eagle Parts for Native American Religious
Purposes''--This application form is used by enrolled members of
federally recognized Tribes to obtain authorization to acquire and
possess eagle feathers and parts from the Service's National Eagle
Repository (NER). The permittee also uses the form to make additional
requests for eagle parts and feathers from the NER. The form collects
the following information: name of the Tribe; Tribal enrollment number
of the individual applicant; a signed Certification of Enrollment;
inmate-specific information in cases where applicants are incarcerated
(inmate number, institution, contact information for the institute's
chaplain); and the specific eagle parts and/or feathers desired by the
applicant. The Service uses the information collected via the form to
verify that the applicant is an enrolled member of a federally
recognized Tribe, and what parts and/or feathers the applicant is
requesting.
(3) Form 3-200-16, ``Take of Depredating Eagles & Eagles that Pose
a Risk to Human or Eagle Health or Safety--Annual Report''--Applicants
use this form to obtain authorization to take (trap, collect, haze)
eagles that depredate on wildlife or livestock, as well as eagles
situated where they pose a threat to human or their own safety. In
addition to the standardized information required by 50 CFR 13.12,
permit application requirements include submission of the following
information: status of other required authorizations (State, Tribal,
local); the species and estimated number of eagles causing the problem;
what the damage or risk consists of; location; method of take;
alternatives taken that were not effective; and a description of the
proposed long-term remedy. The Service uses the information collected
via the form to determine whether the take is necessary to protect the
relevant interests; other alternatives have been considered; and the
method of take is humane and compatible with the preservation of
eagles.
(4) Form 3-200-18, ``Take of Golden Eagle Nests During Resource
Development or Recovery''--This application is used by commercial
entities engaged in resource development or recovery operations, such
as mining or drilling, to obtain authorization to remove or destroy
golden eagle nests. In addition to the standardized information
required by 50 CFR 13.12, permit application requirements include
submission of the following information: location of the property; the
status of other required authorizations; the type of development or
recovery operation; the number of nests to be taken; the activity that
involves the take of the nest; the disposition of the nests once
removed (or destroyed); the duration for which the authorization is
requested; and a description of the mitigation measures that will be
implemented. The Service uses the information collected via the form to
determine whether the take is necessary and will be compatible with the
preservation of eagles.
(5) Form 3-200-77, ``Native American Eagle Take for Religious
Purposes''--Federally recognized Native American Tribes use this form
to apply for authorization to take eagles from the wild for Tribal
religious purposes. In addition to the standardized information
required by 50 CFR 13.12, permit application requirements include
submission of the following information: status of other required
authorizations; location of proposed take; statement of consent by the
land owner or land manager if not on Tribal land; species, number, and
age class of eagles; whether the eagles will be collected alive and
held in captivity; intended disposition of parts and feathers; and the
reason why eagles obtained by other means do not meet the Tribe's
religious needs. The Service uses the information obtained via the form
to determine whether the take is necessary to meet the Tribe's
religious needs, they received consent of the landowner, the take is
compatible with the preservation of eagles, and any eagles kept alive
will be held under humane conditions.
(6) Form 3-200-78, ``Native American Tribal Eagle Aviary''--
Federally recognized Native American Tribes use this form to apply for
authorization to keep live eagles for Tribal religious purposes. In
addition to the standardized information required by 50 CFR 13.12,
permit application requirements include submission of the following
information: descriptions, photographs and/or diagrams of the
enclosures where the eagles will be housed, and number of eagles that
will be kept in each; status of other required authorizations; names
and eagle-handling experience of caretakers; veterinarian who will
provide medical care; and description of the diet and enrichment the
Tribe will provide the eagles. The Service uses the information
collected via the form to ensure the Tribe has the appropriate
facilities and experience to keep live eagles safely and humanely.
(7) Form 3-200-82, ``Bald Eagle or Golden Eagle Transport into the
United States for Scientific or Exhibition Purposes''--This application
is used by researchers and museums to obtain authorization to
temporarily bring eagle specimens into, or take those specimens out of,
the United States. In addition to
[[Page 9954]]
the standardized information required by 50 CFR 13.12, permit
application requirements include submission of the following
information: documentation that the specimen was legally obtained;
documentation that the applicant meets the definition of a ``public''
institution as required under statute; status of other required
authorizations (State, Tribal, local); description of the specimen(s);
country of origin; name of and contact information for the foreign
institution; scientific or exhibition purposes for the transport of
specimens; locations where the item will be exhibited (if applicable);
dates and ports of departure/arrival; and names of persons acting as
agents for the applicant. The Service uses the information collected
via the form to ensure the specimens were legally acquired and will be
transported through U.S. ports that can legally authorize the
transport, the transport will be temporary, as required by statute, and
the specimens will be used for purposes authorized by statute.
(8) Form 3-1552 ``Native American Tribal Eagle Retention''--A
Federal Eagle Remains Tribal Use permit authorizes a federally
recognized Tribe to acquire, possess, and distribute to Tribal members
whole eagle remains found by a Tribal member or employee on the Tribe's
Tribal land for Indian religious use. The applicant must be a federally
recognized Tribal entity under the Federally Recognized Tribal List Act
of 1994, 25 U.S.C. 479a-1, 108 Stat. 4791 (1994). In addition to the
standardized information required by 50 CFR 13.12, the form also
collects the following information: name of the Tribe; name and contact
information for the Tribal leader and primary contact person; whether
the Tribe has already discovered an eagle to hold under the permit; and
if different than what's listed for the primary contact, the address of
the physical location where records will be kept. The Service uses the
information collected via the form to identify which Tribe is applying
for the permit and to inform the Service as to whether the Tribe is
applying before or subsequent to finding the first eagle they want to
retain, allowing the Service to choose the appropriate course of
action.
(9) Form 3-1591, ``Tribal Eagle Retention--Acquisition Form''--This
form provides the Service information needed to track the chain of
custody of eagle remains and ensure the Tribe takes possession of them
as authorized under the permit. The first part of the form (completed
by a Service Office of Law Enforcement (OLE) Officer) collects:
species; sex; age class of eagle; date and location discovered; date
the information was reported to track eagle mortalities; date the
remains were transferred to the Tribe; name and contact information for
the Tribe; and OLE officer name and contact information. The second
part of the form (competed by the Tribe) collects: permit number; date
the Tribe took possession of the eagle; and Principal Tribal Officer's
name, title, and contact information.
(10) Form 3-2480, ``Eagle Recovery Tag''--The form is used to track
dead eagles as they move through the process of laboratory examination
to determine cause of death and are sent to the NER for distribution to
Native Americans for use in religious ceremonies. In addition to the
standardized information required by 50 CFR 13.12, the form also
collects the following information: U.S. Geological Survey band data;
unique ID number assigned; mortality date; species, age, and sex of the
eagle; date recovered; name of person(s) who found and recovered the
eagle; and names and contact information of persons who received the
eagle throughout the chain of custody. The Service uses the information
collected to maintain chain of custody for law enforcement and
scientific purposes.
(11) Form 3-202-11, ``Take of Depredating Eagles & Eagles that Pose
a Risk to Human or Eagle Health or Safety--Annual Report''--Permittees
use this form to report the outcome of their action involving take of
depredating eagles or eagles that pose a risk to human or eagle health
or safety. The form collects the following information: species,
location, date of take, number of eagles, method of take, and final
disposition. The Service uses the information reported via the form to
ascertain whether the planned take was implemented, track how much
authorized take occurred in the eagle management unit and local
population area, and verify the disposition of any eagles taken under
the permit.
(12) Form 3-202-13, ``Eagle Exhibition--Annual Report''--Permittees
use this form to report activities conducted under an Eagle Exhibition
Permit for both Live and Dead Eagles. The form collects the following
information: list of eagles and eagle specimens held under the permit
during the reporting year, and, for each, the date acquired or disposed
of; from whom acquired or to whom transferred; total number of programs
each eagle was used in, or if statically displayed (e.g., in a museum
setting), the number of days the facility was open to the public. The
Service uses the information reported through this form to verify that
eagles held under the permit are used for conservation education.
(13) Form 3-202-14, ``Native American Tribal Eagle Aviary--Annual
Report''--Permittees use this form to report activities conducted under
a Native American Eagle Aviary Permit. The form collects the following
information: a list of eagles held under the permit during the
reporting year, and, for each, the date acquired or disposed of; from
whom acquired or to whom transferred; or other disposition. The Service
uses the information collected via the form to track the live eagles
held by federally recognized Tribes for spiritual and cultural
practices.
(14) Monitoring Requirements--Most permits that authorize take of
eagles or eagle nests require monitoring. We do not require monitoring
for intentional take, including when Native American Tribes take an
eagle as part of a religious ceremony or when falconers trap golden
eagles that are depredating on livestock. A fundamental purpose of
monitoring under eagle take permits is to track levels of take for
population management. For disturbance permits, monitoring also
provides information about whether the permitted activity actually
disturbed eagles, allowing the Service to better understand when these
types of permits may not be needed.
In addition to tracking take at population management scales, the
Service uses data from monitoring lethal take permits to adjust
authorized take levels, compensatory mitigation requirements, and
avoidance and minimization measures as spelled out under the terms of
the permit. With regard to wind industry permits, these data also
enable the Service to improve future fatality estimates through
enhanced understanding of exposure and collision.
(15) Required Notifications--Most permits that authorize take or
possession of eagles require a timely notification to the Service by
email or phone when an eagle possessed under a possession permit or
taken under a permit to take eagles dies or is found dead. These
fatalities are later recorded in reports submitted to the Service as
described above. The timely notifications allow the Service to better
track take and possession levels, and to ensure eagle remains are sent
to either a forensics lab or the NER. Incidental take permittees are
also required to notify the Service via email or phone if a threatened
or endangered species is found in the vicinity of the activity for
which take is permitted. There is no notification requirement for that
beyond reporting each occurrence where take is discovered to have
occurred. The
[[Page 9955]]
Service tracks whether the take level is exceeded or is likely to be
exceeded.
(16) Recordkeeping Requirements--As required by 50 CFR 13.46,
permittees must keep records of the activity as it relates to eagles
and any data gathered through surveys and monitoring, including records
associated with the required internal incident reporting system for
bald eagle and golden eagle remains found and the disposition of the
remains. This information retained by permittees is described above
under reporting requirements.
(17) Amendments--Amendments to a permit may be requested by the
permittee, or the Service may amend a permit for just cause upon a
written finding of necessity. Amendments comprise changes to the permit
authorization or conditions. Those changes may include an increase or
decrease in the authorized take or possession of eagles, proposed
adjustment of permit conditions, or changes to the activity involving
eagles. The permit will specify circumstances under which the Service
will require modifications to avoidance, minimization, or compensatory
mitigation measures or monitoring protocols, which may include, but are
not limited to take levels, location of take, and/or changes in eagle
use of the activity area.
At a minimum, the permit must specify actions to be taken if take
approaches or reaches the amount authorized and anticipated within a
given timeframe. The permittee applies for amendments to the permit by
submitting a description of the modified activity and the changed
conditions affecting eagles. Substantive amendments incur a processing
fee. A permittee is not required to pay a processing fee for minor
changes, such as the legal individual or business name or mailing
address of the permittee. A permittee is required to notify the issuing
office within 10 calendar days of minor changes.
(18) Transfers--In general, permits issued under 50 CFR part 22 are
not transferable. However, when authorized, permits issued under Sec.
22.80 may be transferred by the transferee providing written assurances
of sufficient funding of the avoidance and minimization measures and
commitment to carry out the terms and conditions of the permit.
Copies of the draft forms are available to the public by submitting
a request to the Service Information Collection Clearance Officer using
one of the methods identified in ADDRESSES.
Title of Collection: Eagle Permits and Fees, 50 CFR parts 10, 13,
and 22.
OMB Control Number: 1018-0167.
Form Numbers: FWS Forms 3-200-14, 3-200-15a, 3-200-16, 3-200-18, 3-
200-71, 3-200-72, 3-200-77, 3-200-78, 3-200-82, 3-202-11, 3-202-13, 3-
202-14, 3-202-15, 3-202-16, 3-1552, 3-1591, 3-2480, 3-202-91 (New).
Type of Review: Revision of a currently approved collection.
Respondents/Affected Public: Individuals, businesses, and State/
local/Tribal governments. We expect the majority of applicants seeking
permits will be in the energy production and electrical distribution
business.
Total Estimated Number of Annual Respondents: 8,406.
Total Estimated Number of Annual Responses: 8,406.
Estimated Completion Time per Response: Varies from 15 minutes to
200 hours, depending on activity.
Total Estimated Number of Annual Burden Hours: 32,882.
Respondent's Obligation: Required to obtain or retain a benefit.
Frequency of Collection: On occasion for applications; annually or
on occasion for reports.
Total Estimated Annual Non-hour Burden Cost: $1,737,460 (primarily
associated with application processing and administrative fees).
On September 30, 2022, we published in the Federal Register (87 FR
59598) a proposed rule (RIN 1018-BE70) that announced our intention to
request OMB approval of the revisions to this collection explained
above and the simultaneous renewal of OMB Control No. 1018-0167. In
that proposed rule, we solicited comments for 60 days on the
information collections in this submission, ending on November 29,
2022. Summaries of comments addressing the information collections
contained in this rule, as well as the agency response to those
comments, can be found in the Response to Public Comments section of
this rule, as well as in the information collection request submitted
to OMB on the RegInfo.gov website (https://www.reginfo.gov/public/).
As part of our continuing effort to reduce paperwork and respondent
burdens, we invite the public and other Federal agencies to comment on
any aspect of this information collection, including:
(1) Whether or not the collection of information is necessary for
the proper performance of the functions of the agency, including
whether or not the information will have practical utility;
(2) The accuracy of our estimate of the burden for this collection
of information, including the validity of the methodology and
assumptions used;
(3) Ways to enhance the quality, utility, and clarity of the
information to be collected; and
(4) How the agency might minimize the burden of the collection of
information on those who are to respond, including through the use of
appropriate automated, electronic, mechanical, or other technological
collection techniques or other forms of information technology, e.g.,
permitting electronic submission of response.
Send your written comments and suggestions on this information
collection by the date indicated in DATES to https://www.reginfo.gov/public/do/PRAMain. Find this particular information collection by
selecting ``Currently under 30-day Review--Open for Public Comments''
or by using the search function. Please provide a copy of your comments
to the Service Information Collection Clearance Officer, U.S. Fish and
Wildlife Service, MS: PRB/PERMA (JAO), 5275 Leesburg Pike, Falls
Church, VA 22041-3803 (mail); or by email to [email protected]. Please
reference OMB Control Number 1018-0167 in the subject line of your
comments.
National Environmental Policy Act (42 U.S.C. 4321 et seq.)
We evaluated the environmental impacts of the changes to the
regulations and completed an environmental assessment and finding of no
significant impact. The FONSI is the final step in the NEPA process for
this eagle rule revision process. The FONSI and final environmental
assessment are available in Docket No. FWS-HQ-MB-2020-0023 (available
at https://www.regulations.gov).
Endangered and Threatened Species
Section 7 of the Endangered Species Act of 1973, as amended (16
U.S.C. 1531-43), requires Federal agencies to ``ensure that any action
authorized, funded, or carried out . . . is not likely to jeopardize
the continued existence of any endangered species or threatened species
or result in the destruction or adverse modification of [critical]
habitat'' (16 U.S.C. 1536(a)(2)). Intra-Service consultations and
conferences consider the effects of the Service's actions on listed
species, species proposed for listing, and candidate species. Our final
action of issuing our regulations regarding take of non-ESA-listed
eagles does not authorize, fund, or carry out any activity that may
affect--directly or indirectly--any ESA-listed species or their
critical habitat. See, e.g., Sierra Club v. Bureau of Land Mgmt., 786
F.3d 1219 (9th Cir. 2015). Indeed,
[[Page 9956]]
the Eagle Act does not empower us to authorize, fund, or carry out
project activities by third parties. The Eagle Act empowers us to
authorize take of bald and golden eagles. Thus, we have determined
these revisions have no effect on any listed species, species proposed
for listing, or candidate species or their critical habitat. As a
result, section 7 consultation is not required on this rulemaking
action. As appropriate, we will conduct project-specific, intra-Service
section 7 consultations in the future if our proposed act of issuing a
permit for take of eagles may affect ESA-listed species or critical
habitat.
Government-to-Government Relationship With Tribes
In accordance with the President's memorandum of April 29, 1994,
``Government-to-Government Relations with Native American Tribal
Governments'' (59 FR 22951), E.O. 13175, and the Department of the
Interior's manual at 512 DM 2, we readily acknowledge our
responsibility to communicate meaningfully with recognized Federal
Tribes on a government-to-government basis. In accordance with
Secretary's Order 3206 of June 5, 1997 (American Indian Tribal Rights,
Federal-Tribal Trust Responsibilities, and the Endangered Species Act),
we readily acknowledge our responsibilities to work directly with
Tribes in developing programs for healthy ecosystems, to acknowledge
that Tribal lands are not subject to the same controls as Federal
public lands, to remain sensitive to Indian culture, and to make
information available to Tribes. Although we do not consider this
rulemaking as having Tribal implications according to E.O. 13175
because it is not likely to have ``substantial direct effects'' on any
particular Tribe, we conducted Tribal outreach and invited government-
to-government consultation as if it does.
The Service provided written notification to Tribes about the ANPR
and the proposed rule and offered government-to-government
consultation. The Service conducted Tribal informational webinars on
October 14 and 21, 2021, during the ANPR public comment period as well
as prior to publication of the proposed rule. Seven Tribal
representatives provided written comments. The Service conducted two
additional Tribal informational webinars on October 19 and November 2,
2022, during the proposed rule public comment period as well as
bilateral information sessions when requested by Tribes. Tribal
consulation was requested by one Tribe, which was conducted in
September 2023. No other Tribes requested consultation with the
Service. The Service conducted a final Tribal informational webinar on
December 12, 2023, regarding the changes the Service made in developing
the final rule. Eleven Tribal representatives provided written
comments. As described earlier in this preamble, we have revised the
proposed regulations in response to these comments.
The Service acknowledges our Federal Tribal trust responsibilities
and deeply honors our sovereign nation-to-nation relationship with
Tribes. Throughout all phases of the rulemaking process, the Service
has encouraged and welcomed Tribal engagement, including government-to-
government consultation. To date, we have conducted one government-to-
government consultation. We invite further bilateral government-to-
government consultation at any time.
Energy Supply, Distribution, or Use (E.O. 13211)
E.O. 13211 requires agencies to prepare statements of energy
effects when undertaking certain actions. This rule is a significant
regulatory action under E.O. 12866; however, it will not significantly
affect energy supplies, distribution, or use. The permitting process
streamlines permitting for wind energy and power distribution;
therefore, the rule is intended to ease any administrative burden on
energy development and will not impact it negatively. Therefore, this
action is not a significant energy action, and no statement of energy
effects is required.
List of Subjects
50 CFR Part 13
Administrative practice and procedure, Exports, Fish, Imports,
Plants, Reporting and recordkeeping requirements, Transportation,
Wildlife.
50 CFR Part 22
Exports, Imports, Reporting and recordkeeping requirements,
Transportation, Wildlife.
Regulation Promulgation
Accordingly, we hereby amend parts 13 and 22 of subchapter B of
chapter I, title 50 of the Code of Federal Regulations, as set forth
below:
PART 13--GENERAL PERMIT PROCEDURES
0
1. The authority citation for part 13 continues to read as follows:
Authority: 16 U.S.C. 668a, 704, 712, 742j-l, 1374(g), 1382,
1538(d), 1539, 1540(f), 3374, 4901-4916; 18 U.S.C. 42; 19 U.S.C.
1202; 31 U.S.C. 9701.
0
2. Revise Sec. 13.5 to read as follows:
Sec. 13.5 Information collection requirements.
The Office of Management and Budget (OMB) has approved the
information collection requirements contained in part 13 and assigned
OMB Control Numbers 1018-0022, 1018-0070, 1018-0092, 1018-0093, or
1018-0167 (unless otherwise indicated). Federal agencies may not
conduct or sponsor, and a person is not required to respond to, a
collection of information unless it displays a currently valid OMB
control number. Direct comments regarding the burden estimates or any
other aspect of the information collection to the Service's Information
Collection Clearance Officer at the address provided at 50 CFR 2.1(b).
0
3. Amend Sec. 13.11 by:
0
a. Revising paragraphs (d)(2) and (d)(3)(i); and
0
b. In the table in paragraph (d)(4):
0
i. Removing the 15 entries under ``Bald and Golden Eagle Protection
Act'' and adding 17 new entries in their place; and
0
ii. Revising the footnote 1.
The revisions and additions read as follows:
Sec. 13.11 Application procedures.
* * * * *
(d) * * *
(2) If regulations in this subchapter require more than one type of
permit for an activity and the permits are issued by the same office,
the issuing office may issue one consolidated permit authorizing take
caused by the activity in accordance with Sec. 13.1. You may submit a
single application in these cases, provided that the single application
contains all the information required by the separate applications for
each activity. Where more than one activity is consolidated into one
permit, the issuing office will charge the highest single fee for the
activity for which take is permitted. Administration fees are not
waived.
(3) * * *
(i) We will not charge a permit application fee to any Federal,
Tribal, State, or local government agency or to any individual or
institution acting on behalf of that agency, except administration fees
for permits issued under subpart E of part 22 of this subchapter will
not be waived. If you fail to submit evidence of agency status with
your application, we will require the submission of all processing fees
prior to the acceptance of the
[[Page 9957]]
application for processing, unless otherwise authorized or waived.
* * * * *
(4) * * *
----------------------------------------------------------------------------------------------------------------
Permit
Type of permit CFR citation application fee Administration Amendment fee
\1\ fee \2\
----------------------------------------------------------------------------------------------------------------
* * * * * * *
----------------------------------------------------------------------------------------------------------------
Bald and Golden Eagle Protection Act
----------------------------------------------------------------------------------------------------------------
Eagle Scientific Collecting... 50 CFR part 22.......... 100..............
Eagle Exhibition.............. 50 CFR part 22.......... 75...............
Eagle--Native American 50 CFR part 22.......... No fee...........
Religious Purposes.
Eagle Depredation Permit...... 50 CFR part 22.......... 100..............
Golden Eagle Nest Take........ 50 CFR part 22.......... 100.............. ................. 50.
Eagle Transport--Scientific or 50 CFR part 22.......... 75...............
Exhibition.
Eagle Transport--Native 50 CFR part 22.......... No fee...........
American Religious Purposes.
General Eagle Permit-- 50 CFR part 22.......... 100..............
Disturbance Take.
Specific Eagle Permit-- 50 CFR part 22.......... Commercial--2,500 ................. Commercial--500;
Disturbance Take. ; Noncommercial-- Noncommercial--
500. 150.
General Eagle Permit--Nest 50 CFR part 22.......... 100..............
Take.
Specific Eagle Permit--Nest 50 CFR part 22.......... Commercial--2,500 ................. Commercial--500;
Take (Single nest). ; Noncommercial-- Noncommercial--
500. 150.
Specific Eagle Permit Eagle-- 50 CFR part 22.......... 5,000............ ................. 500.
Nest Take (Multiple nests).
General Eagle Permit-- 50 CFR part 22.......... 1,000............ Non-Investor
Incidental Take (Power lines). Owned--2,500;
Investor Owned--
10,000.
General Eagle Permit-- 50 CFR part 22.......... 1,000............ Distributed and
Incidental Take (Wind energy). Community Scale--
2,500; Utility
Scale--10,000.
Specific Eagle Permit-- 50 CFR part 22.......... Tier 1--18,000; 10,000........... 500.
Incidental Take. Tier 2--26,000.
Eagle Take--Exempted under ESA 50 CFR part 22.......... ................. No fee...........
Transfer of a Subpart E Eagle 50 CFR part 22.......... 1,000............
Permit.
* * * * * * *
----------------------------------------------------------------------------------------------------------------
\1\ A reimbursable agreement may be required for specific eagle permits to cover the costs above estimated staff-
hours.
\2\ An administration fee will be assessed at the time of application, in addition to the application fee.
* * * * *
0
4. Amend Sec. 13.12 by:
0
a. Revising paragraph (a)(1)(ii); and
0
b. In table 1 to paragraph (b), removing the 8 entries under ``Eagle
Permits'' and adding in their place 10 new entries.
The revisions and additions read as follows:
Sec. 13.12 General information requirements on applications for
permits.
(a) * * *
(1) * * *
(ii) If the applicant is an individual, the date of birth,
occupation, and any business, agency, organizational, or institutional
affiliation associated with the wildlife or plants to be covered by the
license or permit; or
* * * * *
(b) * * *
Table 1 to Paragraph (b)
------------------------------------------------------------------------
Type of permit Section
------------------------------------------------------------------------
* * * * * * *
Eagle permits:
Scientific or exhibition.............. 22.50.
Indian religious use.................. 22.60.
Falconry purposes..................... 22.70.
Depredation and protection of health 22.100.
and safety.
Permits for incidental take of eagles. 22.200 or 22.210.
Permits for incidental take of eagles 22.200 or 22.210.
by power lines.
Permits for disturbance take of eagles 22.200 or 22.210.
Permits for nest take of eagle........ 22.200 or 22.210.
Permits for golden eagle nest take for 22.325.
resource recovery operations.
Permits for bald eagle take exempted 22.400.
under the Endangered Species Act.
------------------------------------------------------------------------
Sec. 13.24 [Amended]
0
5. Amend Sec. 13.24 in paragraph (c) introductory text by removing
``Sec. 22.80 of this subchapter B'' and adding in its place ``part 22,
subpart E, of this subchapter''.
Sec. 13.25 [Amended]
0
6. Amend Sec. 13.25 in paragraphs (b) introductory text and (f) by
removing ``Sec. 22.80 of this subchapter B'' and adding in its place
``part 22, subpart E, of this subchapter''.
PART 22--EAGLE PERMITS
0
7. The authority citation for part 22 continues to read as follows:
Authority: 16 U.S.C. 668-668d; 703-712; 1531-1544.
[[Page 9958]]
0
8. Amend Sec. 22.6 by:
0
a. Revising the definitions of ``Eagle management unit (EMU)'' and
``Eagle nest'';
0
b. Adding in alphabetic order a definition for ``General permit'';
0
c. Revising the definition of ``In-use nest''; and
0
d. Adding in alphabetic order a definition of ``Incidental take''.
The revisions and additions read as follows:
Sec. 22.6 Definitions.
* * * * *
Eagle management unit (EMU) means a geographically bounded region
within which permitted take is regulated to meet the management goal of
maintaining stable or increasing breeding populations of bald eagles or
golden eagles.
(1) The Atlantic EMU is Connecticut, Delaware, Florida, Georgia,
Maine, Maryland, Massachusetts, New Hampshire, New Jersey, New York,
North Carolina, Pennsylvania, Rhode Island, South Carolina, Vermont,
Virginia, and West Virginia.
(2) The Mississippi EMU is Alabama, Arkansas, Illinois, Indiana,
Iowa, Kentucky, Louisiana, Michigan, Minnesota, Mississippi, Missouri,
Ohio, Tennessee, and Wisconsin.
(3) The Central EMU is Kansas, Nebraska, New Mexico, North Dakota,
Oklahoma, South Dakota, and Texas; portions of Colorado, New Mexico,
and Wyoming east of the Continental Divide; and portions of Montana
east of Hill, Chouteau, Cascade, Meagher, and Park Counties.
(4) The Pacific EMU is Alaska, Arizona, California, Idaho, Nevada,
Oregon, Utah, Washington; portions of Colorado, New Mexico, and Wyoming
west of the Continental Divide; and in Montana Hill, Chouteau, Cascade,
Meagher, and Park Counties and all counties west of those counties.
(5) An EMU may be further divided between north and south along the
40th Parallel.
Eagle nest means any assemblage of materials built, maintained, or
used by bald eagles or golden eagles for the purpose of reproduction.
An eagle nest remains an eagle nest until it becomes so diminished, or
the nest substrate upon which it is built fails, that the nest is no
longer usable and is not likely to become usable to eagles, as
determined by a Federal, Tribal, or State eagle biologist.
* * * * *
General permit means a permit that has nationwide or regional
standard conditions for a category, or categories, of activities that
are substantially similar in nature.
* * * * *
In-use nest means a bald eagle or golden eagle nest that contains
one or more viable eggs or dependent young, or, for golden eagles only,
has had adult eagles on the nest within the past 10 days during the
breeding season.
Incidental take means take that is foreseeable and results from,
but is not the purpose of, an activity.
* * * * *
0
9. Amend Sec. 22.12 by adding paragraph (c) to read as follows:
Sec. 22.12 Illegal activities.
* * * * *
(c) Application for a permit does not release you from liability
for any take that occurs prior to issuance of, or outside the terms of,
a permit.
0
10. Revise the heading of subpart C to read as follows:
Subpart C--Eagle Possession Permit Provisions
Sec. 22.80 [Removed and Reserved]
0
11. Remove and reserve Sec. 22.80.
Sec. 22.85 [Removed and Reserved]
0
12. Remove and reserve Sec. 22.85.
0
13. Add subpart E to read as follows:
Subpart E--Take of Eagles for Other Interests
Sec.
22.200 Specific permits.
22.210 General permits.
22.215 Conditions of permits.
22.220 Compensatory mitigation.
22.250 Permits for incidental take of eagles by wind energy
projects.
22.260 Permits for incidental take of eagles by power lines.
22.280 Permits for disturbance take of eagles.
22.300 Permits for take of eagle nests.
Sec. 22.200 Specific permits.
(a) Purpose. Specific permits authorize the take of bald eagles or
golden eagles for other interests by activities that are described in
the regulations in this subpart. Proponents of projects may apply for a
specific permit if they do not meet eligibility criteria for general
permits described in--or are conducting an activity not identified in--
Sec. 22.250, Sec. 22.260, Sec. 22.280, or Sec. 22.300. Specific
permits may be recommended by the Service or requested by entities that
are eligible for but do not want to obtain a general permit.
(b) Eligibility. To qualify for a specific permit, you must be
conducting an activity identified in Sec. 22.250, Sec. 22.260, Sec.
22.280, or Sec. 22.300. You must also meet any eligibility
requirements identified in the relevant section.
(1) Permits are issued to the individual or entity conducting the
activity, such as the owner or manager of the entity conducting the
activity. The applicant is responsible for compliance with the permit
and must have the authority to implement the required permit
conditions.
(2) Contractors or consultants may assist in completing
applications or conducting work as a subpermittee but may not be a
permit holder.
(3) Applicants may not break down a project into small parts to
minimize the activity.
(4) Applicants may not combine projects if the activities are not
readily identifiable as being part of the same project. If you want to
obtain a consolidated permit for multiple activities, you must first
submit a separate application for each project and request the Service
determine if it is appropriate to consolidate permits.
(5) Specific permits are issued to a single permit holder. If
multiple entities operate a joint project and want to obtain joint
authorization, the application must designate one entity as the permit
holder and that entity must accept the legal liability for the other
entities. The other entities must grant sufficient authority to the
permit holder to carry out any activities required under the permit.
(6) Upon receipt of your application for a specific permit, the
Service may direct you to apply for a general permit or determine that
a permit is not required. The Service will provide a letter of
authorization to keep in your records.
(7) For existing wind energy projects only, projects that are not
eligible for a general permit for incidental take of eagles (Sec.
22.250) may request a Letter of Authorization from the Service to apply
for a general permit. The Service will review and determine if eagle
risk at the project is consistent with the risk expected for general
permits. To request review, you must submit a specific permit
application and request a determination for general permit eligibility.
Your administration fee will not be refunded to cover the cost of
conducting this review. The application fee may be refunded (50 CFR
13.11(d)(1)).
(c) How to apply for a specific permit. (1) Submit a completed
application form as specified in Sec. 22.250(a), Sec. 22.260(a),
Sec. 22.280(a), or Sec. 22.300(a), as applicable, or Form 3-200-71 if
the activity does not correspond with a particular permit type. Submit
forms to the Regional
[[Page 9959]]
Director of the region where you will conduct your activity. If your
activity spans multiple regions, submit your application to the region
of your U.S. mailing address, and the Service will assign the
appropriate administering region. You can find the current contact
information for Regional Directors in Sec. 2.2 of subchapter A of this
chapter.
(2) Your application must include:
(i) A description of the activity that will cause the take to be
authorized, including the location, seasonality, and duration of the
activity.
(A) If applying under Sec. 22.250 for wind energy projects, that
description must include the number of turbines, rotor diameter, hub
height, location coordinates of each turbine, and the datum of these
coordinates.
(B) If applying under Sec. 22.260 for power lines, include the
State and county(ies) of coverage and total miles of transmission and
distribution lines. To the extent known, include the number of miles or
number of poles in eagle-risk areas that are not avian-safe.
(C) If applying under Sec. 22.280 or Sec. 22.300, include the
location of known nest(s) and nest status (e.g., in-use or alternate).
(ii) Justification of why there is no practicable alternative to
take that would protect the interest to be served.
(iii) An eagle impacts assessment, including eagle activity and
eagle use in the project area and a description of methods used to
conduct this assessment. If the Service has officially issued or
endorsed survey, modeling, take-estimation, or other standards for the
activity that will take eagles, you must follow them and include in
your application all the information thereby obtained, unless the
Service waives this requirement for your application.
(iv) Implemented and proposed steps to avoid and minimize to the
maximum degree practicable, compensate for, and monitor impacts on
eagles.
(v) Alternative actions considered and the reasons why those
alternatives are not practicable.
(vi) Any supplemental information necessary for the Service to make
an adequate determination on the application (see Sec. 13.21 of this
subchapter).
(vii) Payment of the required application and administration fees
(see Sec. 13.11(d)(4) of this subchapter) for the appropriate fee
tier, and, if required, proposed compensatory mitigation plan or eagle
credits to be obtained from a Service-approved conservation bank or in-
lieu fee program. All compensatory mitigation must comply with the
provisions of Sec. 22.220. For incidental take permits issued under
Sec. Sec. 22.250 and 22.260:
(A) The Tier 1 application fee is assessed when standardized permit
conditions require negligible modifications, additional environmental
compliance review is not required, and, if required, fatality estimates
require minimal data manipulation.
(B) The Tier 2 application fee is assessed for all other specific
permit incidental take applications that require 275 staff-hours or
fewer for review, including compliance with the procedural requirements
of NEPA. The Service may require applicants to enter into a
reimbursable agreement to cover the costs above 275 staff-hours.
(d) Issuance criteria. Upon receiving a complete application, the
Regional Director will decide whether to issue a permit based on the
general criteria of Sec. 13.21 of this subchapter and whether the
application meets the following requirements:
(1) The applicant is eligible for a specific permit.
(2) The take:
(i) Is necessary to protect a legitimate interest in a particular
locality;
(ii) Results from, but is not the purpose of, the activity; and
(iii) Cannot practicably be avoided.
(3) The amount of take the Service authorizes under the permit is
compatible with the preservation of the bald eagle and the golden
eagle, including consideration of the effects of other permitted take
and other factors affecting bald eagle and golden eagle populations.
(4) The applicant has proposed avoidance and minimization measures
to reduce the take to the maximum degree practicable relative to the
magnitude of the activity's impacts on eagles. These measures must meet
or exceed the requirements of the general permit regulation (Sec.
22.210), except where not practicable.
(5) If compensatory mitigation is required, the applicant has
proposed either to implement compensatory mitigation measures that
comply with the standards in Sec. 22.220 or secure required eagle
credits from a Service-approved conservation bank or in-lieu fee
program. Compensatory mitigation must meet or exceed the requirements
of the general permit regulation (Sec. 22.210), except when the
Service's evaluation of site-specific data indicates a lower mitigation
rate is appropriate.
(6) The applicant has proposed monitoring plans that are sufficient
to determine the effects on eagle(s) of the proposed activity.
(7) The proposed reporting is sufficient for the Service to
determine the effects on eagle(s).
(8) Any additional factors that may be relevant to our decision
whether to issue the permit, including, but not limited to, the
cultural significance of a local eagle population and whether issuance
of a permit would preclude the Service from authorizing take necessary
to protect an interest of higher priority. The Service will prioritize
safety emergencies, Native American Tribal religious use, and public
health and safety.
(e) Modifications to your permit. If the permittee requests
substantive amendments (see Sec. 13.11(d)(5) of this subchapter)
during the permit tenure, the Service will charge an amendment fee. The
Service will charge an amendment fee and an administration fee for
permittee-requested substantive amendments that require new analysis,
such as modifications that result in re-estimating take, re-evaluating
compensatory mitigation requirements, or requiring additional
environmental review to comply with procedural requirements under NEPA.
(f) Tenure. The tenure of each permit will be designated on the
face of the permit. Specific permits may be valid for a maximum of 30
years. Permit tenure may be less, as restricted by the provisions for
specific activities set forth in Sec. 22.250, Sec. 22.260, Sec.
22.280, or Sec. 22.300 or as appropriate to the duration and nature of
the proposed activity, including mitigation requirements.
Sec. 22.210 General permits.
(a) Purpose. General permits authorize the take of bald eagles or
golden eagles for other interests that meet the eligibility
requirements for general permits set forth in Sec. 22.250, Sec.
22.260, Sec. 22.280, or Sec. 22.300.
(b) Eligibility. To qualify for a general permit, you must be
conducting an activity identified in Sec. 22.250, Sec. 22.260, Sec.
22.280, or Sec. 22.300 and meet any additional eligibility
requirements identified in the relevant section.
(1) Permits are issued to the individual or entity conducting the
activity, such as the owner or manager of the entity conducting the
activity. The applicant is responsible for compliance with the permit
and must have the authority to implement the required permit
conditions.
(2) Contractors or consultants may assist in completing
applications or conducting work as a subpermittee but may not be a
permit holder.
(3) Applicants may not break a project into parts to meet general
permit
[[Page 9960]]
eligibility criteria when the entire project would not be eligible.
(4) Applicants may not combine projects if the activities are not
readily identifiable as being part of the same project. If you want to
obtain a consolidated permit for multiple activities, you must apply
for a specific permit.
(5) General permits are issued to a single permit holder. If
multiple entities operate a joint project and want to obtain joint
authorization, the application must designate one entity as the permit
holder and that entity must accept the legal liability for the other
entities. The other entities must grant sufficient authority to the
permit holder to carry out any activities required under the permit.
(6) The Service may notify you in writing that you must apply for a
specific permit if the Service finds that the project does not comply
with the requirements for a general permit.
(c) How to apply. (1) Register with the Service by submitting the
appropriate application form specified in Sec. 22.250(a), Sec.
22.260(a), Sec. 22.280(a), or Sec. 22.300(a) to Headquarters. You can
find the current contact information for Migratory Birds in Sec. 2.1
of subchapter A of this chapter.
(2) Your application must include:
(i) A description of the activity that will cause the take of bald
eagles or golden eagles, including the location, and seasonality.
(A) If applying under Sec. 22.250 for wind energy projects,
include the number of turbines, rotor diameter, hub height, location
coordinates of each turbine, and the datum of these coordinates.
(B) If applying under Sec. 22.260 for power lines, include the
State and county(ies) of coverage and total miles of transmission and
distribution lines. To the extent known, include the number of miles or
number of poles in eagle-risk areas that are not avian-safe.
(C) If applying under Sec. 22.280 or Sec. 22.300, include the
location of known nests and nest status (i.e., in-use or alternate).
(ii) Justification of why there is no practicable alternative to
take that would protect the interest to be served.
(iii) Description of eagle activity and eagle use in the project
area.
(iv) Certification that the activity involving the take of eagles
authorized by the general permit complies with all other applicable
Federal, State, Tribal, and local laws. This includes certifying that
the activity for which take is to be authorized by the general permit
either does not affect a property that is listed, or is eligible for
listing, in the National Register of Historic Places as maintained by
the Secretary of the Interior; or that the applicant has obtained, and
is in compliance with, a written agreement with the relevant State
Historic Preservation Officer or Tribal Historic Preservation Officer
that outlines all measures the applicant will undertake to mitigate or
prevent adverse effects to the historic property.
(v) Payment of required application and administration fees (see
Sec. 13.11(d)(4) of this subchapter).
(vi) A certification that the applicant agrees to acquire eagle
credits, if required, from a Service-approved conservation bank or in-
lieu fee program within 90 days of the effective date of the permit.
(d) Issuance criteria. Upon an applicant registering by submitting
an application under paragraph (c) of this section, the Service will
automatically issue a general permit to authorize the take requested in
the application. In registering, you must certify that you meet the
general criteria of Sec. 13.21 of this subchapter and the following
issuance criteria:
(1) You are conducting an activity that qualifies for a general
permit.
(2) The take:
(i) Is necessary to protect a legitimate interest in a particular
locality;
(ii) Results from, but is not the purpose of, the activity; and
(iii) Cannot practicably be avoided.
(3) The activity is consistent with the requirements applicable to
that activity as specified in Sec. 22.250, Sec. 22.260, Sec. 22.280,
or Sec. 22.300.
(4) You will implement the general permit conditions applicable to
your activity, including required avoidance, minimization, monitoring,
and reporting requirements.
(5) You will obtain any required eagle credits from a Service-
approved conservation bank or in-lieu fee program within 90 days of the
effective date of your permit.
(e) Program continuation. The Service will regularly evaluate
whether the take of bald eagles and golden eagles under general permits
remains compatible with the preservation of eagles. If the Service
finds, through analysis of the best available information, that the
general permit program is not compatible with the preservation of bald
eagles or golden eagles, the Service may suspend issuing general
permits in all or in part after publishing notification in the Federal
Register. The Service may reinstate issuance of general permits after
publishing another notification in the Federal Register or by
promulgating additional rulemaking. If the Service suspends general
permitting, take currently authorized under a general permit remains
authorized until expiration of that general permit, unless you are
notified otherwise.
(f) Tenure. The tenure of each permit will be designated on the
face of the permit. General permits have a maximum tenure of 5 years.
Permit tenure may be less, as restricted by the applicable provisions
in Sec. 22.250, Sec. 22.260, Sec. 22.280, or Sec. 22.300.
Sec. 22.215 Conditions of permits.
(a) Anyone conducting activities under a specific permit (Sec.
22.200) or general permit (Sec. 22.210) is subject to the conditions
set forth in this section. You must also comply with the relevant
conditions set forth in subpart D of part 13 of this subchapter and the
conditions of your general or specific permit.
(1) Your permit will specify the type of take authorized (e.g.,
incidental take, disturbance, nest take) and may specify the amount,
location, or other restrictions on the take authorized. You are not
authorized for any take not specified on the face of your permit.
(2) Your permit will require implementation of avoidance,
minimization, monitoring, and adaptive management measures consistent
with the relevant regulations in this subpart E. This may include
requirements to:
(i) Modify the seasonality, frequency, timing, duration, or other
aspects of your activity.
(ii) Implement measures to avoid and minimize the take or effects
of take on eagles.
(iii) Monitor to determine the effects of the activity on eagles
according to Service-approved protocols.
(iv) Implement an adaptive management plan.
(3) Your permits will specify requirements for reporting and
disposing of any discovered eagle remains or injured eagles.
Requirements may include:
(i) Training onsite personnel and requiring personnel to scan for
discovered eagle remains or injured eagles;
(ii) Collecting information on discovered eagle remains or injured
eagles, including species, condition, discovery date, location, and
other information relevant to eagle identification and determining the
cause of death or injury;
(iii) Reporting discovered eagle remains or injured eagles,
including immediate notification and annual reporting; and
(iv) Disposition of any discovered eagle remains or injured eagles
in accordance with Service instructions, which may include shipping
eagles to
[[Page 9961]]
the National Eagle Repository or other designated facility.
(4) You must comply with all Service reporting requirements. You
must annually report incidental take and disturbance take using Form 3-
202-15. You must report nest take using Form 3-202-16. You must submit
accurate reports within the required timeline.
(5) You must comply with all compensatory mitigation requirements
in accordance with Sec. 22.220, including any additional requirements
contained in Sec. 22.250, Sec. 22.260, Sec. 22.280, or Sec. 22.300.
(6) You must keep records of all activities conducted under this
permit, including those of subpermittees carried out under the
authority of this permit (see Sec. 13.46 of this subchapter). You must
provide records to the Service upon request.
(7) By accepting this permit, you are authorizing the Service to:
(i) Publish the following information in a public list of
permittees: permittee name, permit type, county and State of activity,
and effective date range.
(ii) Inspect the location and records relating to the activity at
the location where those records are kept. Any inspections will occur
during regular business hours (see Sec. 13.21(e) of this subchapter).
(iii) Provide access to Service staff or contractors as part of
participation in the Service's program-wide monitoring. The Service
will provide reasonable notice for requests to access sites and
negotiate with the permittee about practicable and appropriate access
conditions to protect human health and safety and comply with any
physical, logistical, or legal constraints.
(8) You are responsible for ensuring that the activity for which
take is authorized complies with all applicable Federal, Tribal, State,
and local laws, regulations, and permits. You must comply with all
label instructions for handling controlled substances and chemicals,
including pesticides.
(9) Permits are issued to the entity or individual conducting the
action.
(i) The Principal Officer is the chief operating officer
responsible for the permit application and any permitted activities.
The Principal Officer is responsible for compliance with all conditions
of authorization, including the conditions listed here and any permit
conditions. The Principal Officer must have the authority to implement
all conditions and is legally liable for any subpermittee conducting
activities under the permit.
(ii) The authority of this authorization may be exercised by
subpermittees. A subpermittee is any person who is employed by the
authorized entity to conduct the activities specified or any person
designated as a subpermittee in writing by the Principal Officer.
Subpermittee-designation letters must identify who can conduct what
activities and list any restrictions on the dates, locations, or types
of activities the subpermittee may conduct.
(iii) The Principal Officer is responsible for any subpermittee who
is conducting authorized activities. Subpermittees must have the
conditions of authorization and, if applicable, a copy of the permit
readily available. Subpermittees who are not employees must also have a
subpermittee-designation letter.
(b) The Service may amend, suspend, or revoke a permit issued under
this subpart if new information indicates that revised permit
conditions are necessary, or that suspension or revocation is
necessary, to safeguard local or regional eagle populations. This
provision is in addition to the general criteria for amendment,
suspension, and revocation of Federal permits set forth in Sec. Sec.
13.23, 13.27, and 13.28 of this subchapter.
(c) Notwithstanding the provisions of Sec. 13.26 of this
subchapter, you remain responsible for all outstanding monitoring
requirements and mitigation measures required under the terms of the
permit for take that occurs prior to cancellation, expiration,
suspension, or revocation of the permit.
Sec. 22.220 Compensatory mitigation.
(a) Your permit conditions may include a requirement to compensate
for the take of eagles.
(1) Any permit authorizing take that would exceed the applicable
EMU take limit will require compensatory mitigation, except in
circumstances where the action is considered in the best interest of an
eagle. Compensatory mitigation for this purpose must ensure the
preservation of the affected eagle species by mitigating an amount
equal to or greater than the authorized or expected take. Compensatory
mitigation must either reduce another ongoing form of mortality or
increase the eagle population of the affected species. Compensatory
mitigation for golden eagles must be performed at a 1.2:1 (mitigation:
take) ratio.
(2) A permit may require compensatory mitigation when the Service
determines, according to the best available information, that the take
authorized by the permitted activity is not consistent with maintaining
the persistence of the local area population of an eagle species.
(b) All required compensatory mitigation actions must:
(1) Be contingent upon application of avoidance and minimization
measures to reduce the take to the maximum degree practicable relative
to the magnitude of the project's impacts on eagles.
(2) Be sited within:
(i) The same EMU where the permitted take will occur; or
(ii) Another EMU if the Service has reliable data showing that the
population affected by the take includes individuals that are
reasonably likely to use that EMU during part of their seasonal
migration.
(3) If required by the Service, be sited within a specified local
area population.
(4) Use the best available science in formulating, crediting, and
monitoring the long-term effectiveness of mitigation measures.
(5) Be additional to and improve upon the baseline conditions for
the affected eagle species in a manner that is demonstrably new and
would not have occurred without the compensatory mitigation.
(6) Be durable and, at a minimum, maintain its intended purpose for
as long as required by the mitigation conditions in the permit.
(7) Include mechanisms to account for and address uncertainty and
risk of failure of a compensatory mitigation measure.
(8) Include financial assurances that the required compensatory
mitigation measures will be implemented in full.
(c) Compensatory mitigation must be approved by the Service and may
include conservation banks, in-lieu fee programs, or permittee-
responsible mitigation as mitigation providers.
(1) General permittees meet this requirement by obtaining required
credits from a Service-approved, third-party mitigation provider.
Specific permittees can meet this requirement by obtaining required
credits from a Service-approved, third-party mitigation provider or
meeting the requirements to be a permittee-responsible mitigation
provider as described in paragraph (c)(2) of this section. Third-party
mitigation providers (e.g., in-lieu fee programs and conservation
banks) obtain Service approval by meeting the requirements to be a
mitigation provider as described in paragraph (c)(2) of this section.
(2) To obtain approval as a mitigation provider, potential
providers must submit a mitigation plan to the Service that
demonstrates how the standards set forth in paragraph (b) of this
section will be met. At a minimum, this must include a description of
the mitigation, the benefit to eagles, the locations where
[[Page 9962]]
projects will be implemented, the EMU and local area population
affected, the number of credits provided, and an explanation of the
rationale for the number of eagle credits provided. The Service must
approve the mitigation plan prior to implementation.
Sec. 22.250 Permits for incidental take of eagles by wind energy
projects.
(a) Purpose. The regulations in this section authorize the
incidental killing or injury of bald eagles and golden eagles
associated with the operation of wind energy projects. Apply using Form
3-200-71.
(b) Definition. The following term used in this section has the
meaning set forth in this paragraph (b):
Existing project. Infrastructure that was operational prior to May
13, 2024, as well as infrastructure that was sufficiently far along in
the planning process on that date that complying with new requirements
would be impracticable, including if an irreversible or irretrievable
commitment of resources has been made (e.g., site preparation was
already underway or infrastructure was partially constructed).
(c) Eligibility for a general permit. To qualify for a general
permit, you must meet the requirements of Sec. 22.210, be located in
the contiguous 48 States, not have discovered four or more eagles of
one species in the previous 5 years per paragraph (d)(3) of this
section, and:
(1) Be a project applying for a general permit for the first time,
and all turbines associated with the project are:
(i) At least 2 miles from a golden eagle nest and at least 660 feet
from a bald eagle nest; and
(ii) Located in areas characterized by seasonal relative abundance
values that are less than the relative abundance values for the date
range for each species in tables 1 and 2:
Table 1 to Paragraph (c)(1)(ii)--Relative Abundance Value Thresholds for
Bald Eagles Throughout the Year
------------------------------------------------------------------------
Bald Eagle
Date range relative
abundance
------------------------------------------------------------------------
1. February 15-May 23................................... 0.821
2. May 24-July 19....................................... 0.686
3. July 20-December 20.................................. 0.705
4. December 21-February 14.............................. 1.357
------------------------------------------------------------------------
Table 2 to Paragraph (c)(1)(ii)--Relative Abundance Value Thresholds for
Golden Eagles Throughout the Year
------------------------------------------------------------------------
Golden Eagle
Date range relative
abundance
------------------------------------------------------------------------
1. February 8-June 6.................................... 0.081
2. June 7-August 30..................................... 0.065
3. August 31-December 6................................. 0.091
4. December 7-February 7................................ 0.091
------------------------------------------------------------------------
(2) Be a project currently authorized under a general permit that:
(i) Has discovered fewer than four eagles (either eagle remains or
injured eagles) of any one species during the previous general permit
tenure;
(ii) Had no lapse in general-permit coverage; and
(iii) Ensures that any turbines not authorized on the previous
general permit meet the issuance criteria in paragraph (c)(1) of this
section.
(3) Be an existing project that has received a letter of
authorization from the Service (see Sec. 22.200(b)(7)).
(d) Discovered eagle provisions for general permits. You must
implement procedures to discover eagle remains and injured eagles in
accordance with Sec. 22.215(a)(3) and as required by your permit
conditions. In following those protocols:
(1) You must include in your annual report the discovery of any
eagle remains or injured eagles.
(2) If you discover eagle remains or injured eagles of three eagles
of any one species during the tenure of a general permit, you must
notify the Service in writing within 2 weeks of discovering the take of
a third eagle and implement adaptive management measures. When
notifying the Service, you must include the reporting data required by
your permit conditions, your adaptive management plan, and a
description and justification of the adaptive management approaches you
will implement for the remaining duration of your general permit.
(3) If you discover eagle remains or injured eagles of four eagles
of any one species during the tenure of a general permit, you must
notify the Service in writing within 2 weeks of discovering the take of
the fourth eagle. When notifying the Service, you must include the
reporting data required by your permit conditions, your adaptive
management plan, and a description and justification of the adaptive
management approaches you will implement for the remaining duration of
your general permit term. The project will remain authorized to
incidentally take eagles through the term of the existing general
permit but will not be eligible for future general permits. You may
instead apply for a specific permit for incidental take at that
project. You may request reconsideration of general-permit eligibility
by following the review procedures set forth at Sec. 13.29 of this
subchapter, including providing the information required in Sec.
13.29(b)(3).
(4) If the Service conducts monitoring at a wind project, eagle
remains or injured eagles discovered by the Service, or Service
contractor, are not attributed to the project for the purposes of this
paragraph (d), unless the Service determines the eagles were also
discovered, or were likely to have been discovered, by required
monitoring efforts at the project.
(e) Eligibility for a wind energy specific permit. To qualify for a
specific permit, you must meet the requirements of Sec. 22.200. In
determining whether to issue a permit, the Service will review the
application materials provided,
[[Page 9963]]
including the eagle impacts assessment. The Service will determine,
using the best available data, the expected take of eagles by the
proposed activity.
(f) Wind energy permit conditions. The following conditions apply
to all general and specific permits. Specific permits may include
additional project-specific permit conditions.
(1) Develop and implement an adaptive management plan. An adaptive
management plan applies the best available science and monitoring to
refine project operations and practices. Plans identify criteria for
implementation of the mitigation hierarchy, including avoidance,
minimization, and compensation to remain consistent with permit
conditions and the preservation of eagles.
(2) Remove and avoid creating anthropogenic features that increase
the risk of eagle take by attracting eagles to the project site or
encouraging foraging, roosting, or nesting behaviors.
(3) Minimize collision and electrocution risks, including
collisions with turbines, vehicles, towers, and power lines.
(4) Comply with all relevant regulations and permit conditions in
part 21 of this subchapter.
(5) Submit required reports to the Service by the applicable
deadline.
(6) Pay the required application and administration fees (see Sec.
13.11(d)(4) of this subchapter).
(7) Implement required compensatory mitigation. You must keep
records to document compliance with this requirement and provide them
to the Service with your annual report.
(i) For wind energy specific permits, you must submit a plan to the
Service in accordance with Sec. 22.200(c) and implement the
compensatory-mitigation requirements included on the face of your
permit.
(ii) For wind energy general permits, you must obtain eagle credits
from a Service-approved conservation bank or in-lieu fee program based
on the hazardous volume of the project (in cubic kilometers). The
hazardous volume of a project is calculated as the number of turbines
multiplied by 0.200[pi](d/2)[supcaret]2 where d is the diameter of the
blades in kilometers. You must obtain eagle credits at the following
rates: Atlantic/Mississippi EMUs: 6.02 eagles/km\3\, Central EMU: 7.46
eagles/km\3\, and Pacific EMU: 11.12 eagles/km\3\.
(g) Tenure of permits. General permits are valid for 5 years from
the date of registration. Specific permits may be valid for up to 30
years.
Sec. 22.260 Permits for incidental take of eagles by power lines.
(a) Purpose. The regulations in this section authorize the
incidental killing or injury of bald eagles and golden eagles
associated with power line activities. Apply using Form 3-200-71.
(b) Definitions. The following terms used in this section have the
meanings set forth in this paragraph (b):
Avian-safe. A power-pole configuration designed to minimize avian
electrocution risk by providing sufficient separation between phases
and between phases and grounds to accommodate the wrist-to-wrist or
head-to-foot distance of the bird. For eagles, this is 150 centimeters
of horizontal separation and 100 centimeters of vertical separation. If
sufficient separation cannot be provided, exposed parts that conduct
electricity must be covered to reduce electrocution risk. If covers are
used, they must be maintained in good condition. For conversions from
an above-ground line to a buried line, the buried portion is considered
``avian-safe.'' For purposes of the regulations in this section,
``avian-safe'' means safe for eagles.
Collision response strategy. A plan that describes the process the
permittee will follow to identify whether a collision-caused injury or
mortality has occurred, to evaluate factors that contributed to the
collision, and to implement risk-reduction measures commensurate with
the collision risk.
Proactive retrofit strategy. A plan to convert existing
infrastructure to avian-safe infrastructure within a set timeline. The
strategy must identify a baseline of poles to be proactively retrofit.
The existing-infrastructure baseline must include all poles that are
not avian-safe for eagles located in areas identified as high risk to
eagles and may also include other poles in the service area.
Reactive retrofit strategy. A plan to respond to incidents where
eagles are electrocuted or killed. The reactive retrofit strategy must
include information on how eagle electrocutions are detected and
identified. Determining which poles to retrofit must be based on the
risk to eagles and not on other factors (e.g., convenience or cost).
The pole that caused the electrocution must be retrofitted unless the
pole is already avian-safe. A total of 13 poles or a half-mile segment
must be retrofitted, whichever is less, prioritizing the highest risk
poles closest to the electrocution event.
Shooting response strategy. A plan that describes the process the
permittee will follow when eagles are found killed or injured near
power-line infrastructure to identify if shooting is suspected, to
communicate with law enforcement, and to identify and implement
appropriate shooting reduction measures.
(c) Eligibility for a general permit for incidental take. To
qualify for a general permit, you must meet the requirements of Sec.
22.210.
(d) General permit conditions for power lines. Project permittees
must:
(1) Develop a reactive retrofit strategy and implement that
strategy following each discovery of an electrocuted eagle. The
investigation, documentation, and retrofit design selection must be
completed within 90 days of the incident. The retrofit must be
implemented within 1 year of the incident and remain effective for 30
years.
(2) Implement a proactive retrofit strategy to convert all
existing-infrastructure-baseline poles to avian-safe. Retrofits must
remain effective for 30 years.
(i) Investor-owned utilities must retrofit all existing-
infrastructure-baseline poles within 50 years. Ten percent of baseline
poles must be converted to avian-safe during each permit tenure unless
extenuating circumstances apply.
(ii) Non-investor-owned utilities must retrofit all existing-
infrastructure-baseline poles within 75 years. Seven percent of
baseline poles must be converted to avian-safe during each permit
tenure unless extenuating circumstances apply.
(3) Implement an eagle collision response strategy. Within 90 days
of a collision, you must complete an investigation where the collision
occurred by documenting the factors contributing to the collision and
identifying appropriate risk-reduction measures. You must implement
selected risk-reduction measures at the location of the collision
within 1 year of the incident.
(4) Implement an eagle shooting response strategy. The strategy
must include a protocol for immediately contacting the Office of Law
Enforcement (in no case more than 72 hours from discovery) when finding
eagle remains or an injured eagle near power line infrastructure in
circumstances that suggest the eagle may have been shot. If multiple
shooting events occur in the service area during the permit tenure, the
strategy should describe and provide for the implementation of
reasonable shooting-reduction measures.
(5) Train personnel to scan for eagle remains when onsite and
implement internal reporting and recordkeeping procedures for
discovered eagles.
[[Page 9964]]
(6) Ensure that all new construction and rebuild or replacement of
poles in areas of high risk for eagles is avian-safe unless this
requirement would unduly impact human health and safety, require overly
burdensome engineering, or have significant adverse effects on
biological, cultural, or historical resources.
(7) For new construction and rebuild, reconstruction, or
replacement projects, incorporate information on eagles into siting and
design considerations. Minimize eagle risk by siting away from eagle-
use areas (e.g., nests and winter roosts), accounting for the risk to
and population status of the species, unless this requirement would
unduly impact human health and safety; require overly burdensome
engineering; or have significant adverse effects on biological,
cultural, or historical resources.
(8) Comply with all relevant regulations and permit conditions of
part 21 of this subchapter.
(9) Submit required reports to the Service using Form 3-202-15.
(10) Pay the required application and administration fee as set
forth in Sec. 13.11(d)(4) of this subchapter.
(e) Specific permit for incidental take--(1) Eligibility. Any
entity conducting power line activities that meet the requirements of
Sec. 22.200 may apply for a specific permit.
(2) Conditions. You must comply with the conditions required in
Sec. 22.200. Your permit conditions will include the relevant general-
permit conditions from paragraph (d) of this section. Compensatory
mitigation may be required when appropriate, including if general
permit conditions cannot be met.
(f) Tenure of permits. Power line general permits are valid for 5
years. Specific permits may be valid for up to 30 years.
Sec. 22.280 Permits for disturbance take of eagles.
(a) Purpose. The regulations in this section authorize the take of
bald eagles or golden eagles by disturbance, as defined in Sec. 22.6.
Apply using Form 3-200-91. Permits to authorize disturbance associated
with hazing eagles or eagle nest take are not authorized under this
section. A permit is not required when an activity that may ordinarily
disturb eagles is ongoing at the time an eagle pair initiates nesting
because the nesting eagles are presumed to tolerate the activity.
(b) Eligibility for a general permit for disturbance. To qualify
for a general permit, you must meet the requirements of Sec. 22.210,
and your activities must comply with the provisions set forth in
paragraphs (b)(1) through (9) of this section. If permanent loss of a
territory may occur, a specific permit is recommended because general
permits for disturbance do not authorize the permanent loss of a
territory. General permits are not available if the nest is located in
Indian country (18 U.S.C. 1151), unless the Tribe is the applicant. The
following activities are eligible for a general permit:
(1) Building construction and maintenance within 660 feet of a bald
eagle nest.
(2) Linear infrastructure construction and maintenance (e.g.,
roads, rail, trails, power lines, and other utilities) within 660 feet
of a bald eagle nest.
(3) Alteration of shorelines and water bodies (e.g., shorelines,
wetlands, docks, moorings, marinas, and water impoundment) within 660
feet of a bald eagle nest.
(4) Alteration of vegetation (e.g., mowing, timber operations, and
forestry practices) within 660 feet of a bald eagle nest.
(5) Motorized recreation (e.g., snowmobiles, motorized watercraft,
etc.) within 330 feet of an in-use bald eagle nest.
(6) Nonmotorized recreation (e.g., hiking, camping, fishing,
hunting, canoeing, etc.) within 330 feet of an in-use bald eagle nest.
(7) Aircraft operation (e.g., helicopters and fixed-wing aircraft)
within 1,000 feet of an in-use bald eagle nest.
(8) Prescribed burn operations within 660 feet of a bald eagle
nest.
(9) Loud, intermittent noises (e.g., blasting) within one-half-mile
of an in-use bald eagle nest.
(c) Eligibility for a specific permit for disturbance. To qualify
for a specific permit, you must meet the requirements of Sec. 22.200.
Specific permits are for disturbance of a golden eagle nest,
disturbance of a bald eagle nest by an activity not specified in
paragraph (b) of this section, or disturbance of eagles caused by
physical or functional elimination of all foraging area within a
territory.
(d) Disturbance permit conditions. (1) To the maximum degree
practicable, implement measures to avoid and minimize nest disturbance,
including disturbance due to noise from human activities, visibility of
human activities, proximity of activities to the nest, habitat
alteration, and any indirect stressors.
(2) Avoid activities that may negatively affect the nesting
substrate, including the survival of the nest tree.
(3) Monitor in-use nests sufficiently to determine whether
nestlings have fledged from the nest. Include this information in your
annual report.
(e) Reporting. You must submit an annual report using Form 3-202-
15. The annual report is due on the date specified on your permit or
prior to requesting renewal of your permit, whichever is first.
(f) Tenure of permits. General permits for disturbance issued under
the regulations in this section are valid for a maximum of 1 year. The
tenure of specific permits for disturbance is set forth on the face of
the permit and may not exceed 5 years.
Sec. 22.300 Permits for take of eagle nests.
(a) Purpose. This section authorizes the take of a bald eagle nest
or a golden eagle nest, including relocation, removal, and otherwise
temporarily or permanently preventing eagles from using the nest
structure for breeding, when there is no practicable alternative that
would protect the interest to be served. Apply using Form 3-200-72.
(b) Definitions. The following terms used in this section have the
meanings set forth in this paragraph (b):
Nest take for emergency. Take of an in-use or alternate eagle nest
when necessary to alleviate an existing safety emergency for humans or
eagles or to prevent a rapidly developing situation that is likely to
result in a safety emergency for humans or eagles.
Nest take for health and safety. Take of an eagle nest when the
removal is necessary to ensure public health and safety. Nest take for
health and safety is limited to in-use nests prior to egg laying or
alternate nests.
Nest take for human-engineered structure. Take of an eagle nest
built on a human-engineered structure that creates, or is likely to
create, a functional hazard that renders the structure inoperable for
its intended use. Take is limited to in-use nests prior to egg-laying
or alternate nests.
Nest take for species protection. Take of an eagle nest when nest
removal is necessary to protect a species federally protected under the
Endangered Species Act of 1973, as amended (16 U.S.C. 1531-1544) and
included on the List of Endangered and Threatened Wildlife (at Sec.
17.11 of this subchapter). Take is limited to in-use nests prior to egg
laying or alternate nests.
Other purposes. Take of an alternate eagle nest, provided the take
is necessary to protect an interest in a particular locality and the
activity necessitating the take or the mitigation for the take will,
with reasonable certainty, provide a net benefit to eagles.
(c) Eligibility for a general permit for nest take. To qualify for
a general permit, you must meet the requirements of Sec. 22.210.
[[Page 9965]]
(1) General permits are available for bald eagle nest take for
emergency, nest take for health and safety, or nest take for a human-
engineered structure, or, if located in Alaska, other purposes.
(2) General permits are not available for take of golden eagle
nests. General permits are not available for bald eagle nests if
removal may result in the complete loss of a territory.
(3) General permits are not available if the nest is located in
Indian country (18 U.S.C. 1151), unless the Tribe is the applicant.
(d) Eligibility for a specific permit for nest take. To qualify for
a specific permit, you must meet the requirements of Sec. 22.200.
Specific permits are required for take of a golden eagle nest for any
purpose, nest take for species protection, and, except in Alaska, nest
take for other purposes.
(e) Permits for species protection. If you are applying for a nest-
take permit for species protection, you must:
(1) Be a Federal, State, or Tribal agency responsible for
implementing actions for the protection of the species of concern.
(2) Include documentation that:
(i) Describes relevant management efforts to protect the species of
concern.
(ii) Identifies and describes how the nesting eagles are a limiting
factor to recovery of the species using the best available scientific
information and data.
(iii) Explains how take of eagle nests is likely to have a positive
effect on recovery for the species of concern.
(f) Permit conditions for nest take. Permit conditions may include
requirements to:
(1) Adjust the timing of your activity to minimize the effects of
nest take on eagles.
(2) Place an obstruction in the nest or nest substrate.
(3) Minimize or deter renesting attempts that would cause the same
emergency, safety, or functional hazard.
(4) Relocate the nest or provide suitable nesting substrate within
the same territory.
(5) Remove chicks or eggs from an in-use nest for immediate
transport to a foster nest, rehabilitation facility, or as otherwise
directed by the Service.
(6) If nestlings or eggs are relocated with a nest or to a foster
nest, monitor the nest to ensure adults are tending to nestlings or
eggs.
(7) Monitor the area near the nest removal for one or more seasons
to determine the effect on eagles.
(8) Submit an annual report using Form 3-202-16.
(g) Tenure of permits. General permits issued under this section
are valid until the start of the next breeding season, not to exceed 1
year. The tenure of specific permits is set forth on the face of the
permit and may not exceed 5 years.
Sec. 22.75 [Redesignated as Sec. 22.235]
0
14. Redesignate Sec. 22.75 as Sec. 22.325 and transfer to subpart E.
0
15. Amend newly designated Sec. 22.325 by:
0
a. Revising the section heading; and
0
b. In the introductory text, removing the three sentences that follow
the first sentence.
The revision reads as follows:
Sec. 22.325 Permits for golden eagle nest take for resource recovery
operations.
* * * * *
Sec. 22.90 [Redesignated as Sec. 22.400]
0
16. Redesignate Sec. 22.90 as Sec. 22.400 and transfer to subpart E.
Sec. 22.400 [Amended]
0
17. Amend newly designated Sec. 22.400 in paragraphs (a) and (b) by
removing the words ``the effective date of 50 CFR 22.80'' and adding in
their place the words ``November 10, 2009''.
Shannon A. Estenoz,
Assistant Secretary for Fish and Wildlife and Parks.
[FR Doc. 2024-02182 Filed 2-8-24; 8:45 am]
BILLING CODE 4333-15-P