Listing Endangered and Threatened Species and Designating Critical Habitat; Implementing Changes to the Regulations for Designating Critical Habitat, 7413-7440 [2016-02680]
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Vol. 81
Thursday,
No. 28
February 11, 2016
Part II
Department of the Interior
Fish and Wildlife Service
Department of Commerce
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National Marine Fisheries Service
50 CFR Part 424
Listing Endangered and Threatened Species and Designating Critical
Habitat; Implementing Changes to the Regulations for Designating Critical
Habitat; Final Rule
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Federal Register / Vol. 81, No. 28 / Thursday, February 11, 2016 / Rules and Regulations
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
DEPARTMENT OF COMMERCE
National Marine Fisheries Service
50 CFR Part 424
[Docket No. FWS–HQ–ES–2012–0096;
Docket No. 120106025–5640–03;
4500030114]
RIN 1018–AX86; 0648–BB79
Listing Endangered and Threatened
Species and Designating Critical
Habitat; Implementing Changes to the
Regulations for Designating Critical
Habitat
U.S. Fish and Wildlife Service,
Interior; National Marine Fisheries
Service, Commerce.
ACTION: Final rule.
AGENCY:
We, the U.S. Fish and
Wildlife Service (FWS) and the National
Marine Fisheries Service (NMFS)
(collectively referred to as the
‘‘Services’’ or ‘‘we’’), amend portions of
our regulations that implement the
Endangered Species Act of 1973, as
amended (Act). The revised regulations
clarify, interpret, and implement
portions of the Act concerning the
procedures and criteria used for adding
species to the Lists of Endangered and
Threatened Wildlife and Plants and
designating and revising critical habitat.
Specifically, the amendments make
minor edits to the scope and purpose,
add and remove some definitions, and
clarify the criteria and procedures for
designating critical habitat. These
amendments are based on the Services’
review of the regulations and are
intended to clarify expectations
regarding critical habitat and provide for
a more predictable and transparent
critical habitat designation process.
Finally, the amendments are also part of
the Services’ response to Executive
Order 13563 (January 18, 2011), which
directs agencies to review their existing
regulations and, among other things,
modify or streamline them in
accordance with what has been learned.
DATES: Effective date: This rule is
effective March 14, 2016. Applicability
date: This rule applies to rules for
which a proposed rule was published
after March 14, 2016.
ADDRESSES: Public input and a list of
references cited for this final rule are
available on the Internet at https://
www.regulations.gov. Supporting
documentation used in the preparation
of this rule will be available for public
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SUMMARY:
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inspection, by appointment, during
normal business hours at: U.S. Fish and
Wildlife Service, Division of
Conservation and Classification, 5275
Leesburg Pike; Falls Church, VA 22041–
0041, telephone 703/358–2171;
facsimile 703/358–1735 and National
Marine Fisheries Service, Office of
Protected Resources, 1315 East-West
Highway, Silver Spring, MD 20910,
telephone 301–713–1401; facsimile
301–713–0376.
FOR FURTHER INFORMATION CONTACT:
Douglas Krofta, U.S. Fish and Wildlife
Service, Division of Conservation and
Classification, 5275 Leesburg Pike, Falls
Church, VA 22041, telephone 703/358–
2527; facsimile 703/358–1735; or Marta
Nammack, National Marine Fisheries
Service, Office of Protected Resources,
1315 East-West Highway, Silver Spring,
MD 20910, telephone 301/427–8469;
facsimile 301/713–0376. If you use a
telecommunications device for the deaf
(TDD), call the Federal Information
Relay Service (FIRS) at 800–877–8339.
SUPPLEMENTARY INFORMATION: This
document is one of three listed below,
of which two are final rules and one is
a final policy:
• A final rule that amends the
regulations governing section 7
consultation under the Endangered
Species Act to revise the definition of
‘‘destruction or adverse modification’’ of
critical habitat. The previous regulatory
definition had been invalidated by
several courts for being inconsistent
with the language of the Act. That final
rule amends title 50 of the Code of
Federal Regulations (CFR) at part 402.
The Regulation Identifier Numbers
(RINs) are 1018–AX88 and 0648–BB80,
and the final rule may be found on
https://www.regulations.gov at Docket
No. FWS–R9–ES–2011–0072.
• A final rule that amends the
regulations governing the designation of
critical habitat under section 4 of the
Act. A number of factors, including
litigation and the Services’ experiences
over the years in interpreting and
applying the statutory definition of
‘‘critical habitat,’’ highlighted the need
to clarify or revise the regulations. This
final rule (this document) amends 50
CFR part 424. It is published under RINs
1018–AX86 and 0648–BB79 and may be
found on https://www.regulations.gov at
Docket No. FWS–HQ–ES–2012–0096 or
at Docket No. NOAA–NMFS–2014–
0093.
• A final policy pertaining to
exclusions from critical habitat and how
we consider partnerships and
conservation plans, conservation plans
permitted under section 10 of the Act,
Tribal lands, national-security and
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homeland-security impacts and military
lands, Federal lands, and economic
impacts in the exclusion process. This
final policy complements the revised
regulations at 50 CFR part 424 and
clarifies expectations regarding critical
habitat, and provides for a more
predictable and transparent exclusion
process. The policy is published under
RIN 1018–AX87 and 0648–BB82 and
may be found on https://
www.regulations.gov at Docket No.
FWS–R9–ES–2011–0104.
Background
The Endangered Species Act of 1973,
as amended (16 U.S.C. 1531 et seq.),
states that the purposes of the Act are
to provide a means to conserve the
ecosystems upon which listed species
depend, to develop a program for the
conservation of listed species, and to
achieve the purposes of certain treaties
and conventions. Moreover, the Act
states that it is the policy of Congress
that the Federal Government will seek
to conserve threatened and endangered
species, and use its authorities to further
the purposes of the Act.
In passing the Act, Congress viewed
habitat loss as a significant factor
contributing to species endangerment.
Habitat destruction and degradation
have been a contributing factor causing
the decline of a majority of species
listed as threatened or endangered
species under the Act (Wilcove et. al.
1998). The present or threatened
destruction, modification, or
curtailment of a species’ habitat or range
is included in the Act as one of the
factors on which to base a determination
of threatened or endangered species
status. One of the tools provided by the
Act to conserve species is the
designation of critical habitat.
The purpose of critical habitat is to
identify the areas that are essential to
the species’ recovery. Once critical
habitat is designated, it can contribute
to the conservation of listed species in
several ways. Specifying the geographic
location of critical habitat facilitates
implementation of section 7(a)(1) of the
Act by identifying areas where Federal
agencies can focus their conservation
programs and use their authorities to
further the purposes of the Act.
Designating critical habitat also helps
focus the conservation efforts of other
conservation partners, such as State and
local governments, nongovernmental
organizations, and individuals.
Furthermore, when designation of
critical habitat occurs near the time of
listing, it provides a form of early
conservation planning guidance (e.g.,
identifying some of the areas that are
needed for recovery, the physical and
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biological features needed for the
species’ life history, and special
management considerations or
protections) to bridge the gap until the
Services can complete recovery
planning.
In addition to serving as an
educational tool, the designation of
critical habitat also provides a
significant regulatory protection—the
requirement that Federal agencies
ensure, in consultation with the
Services under section 7(a)(2) of the Act,
that their actions are not likely to
destroy or adversely modify critical
habitat. The Federal Government,
through its role in water management,
flood control, regulation of resources
extraction and other industries, Federal
land management, and the funding,
authorization, and implementation of
myriad other activities, may propose
actions that are likely to affect critical
habitat. The designation of critical
habitat ensures that the Federal
Government considers the effects of its
actions on habitat important to species’
conservation and avoids or modifies
those actions that are likely to destroy
or adversely modify critical habitat.
This benefit is especially valuable
when, for example, species presence or
habitats are ephemeral in nature,
species presence is difficult to establish
through surveys (e.g., when a plant’s
‘‘presence’’ is sometimes limited to a
seed bank), or protection of unoccupied
habitat is essential for the conservation
of the species.
The Secretaries of the Interior and
Commerce (the ‘‘Secretaries’’) share
responsibilities for implementing most
of the provisions of the Act. Generally,
marine and anadromous species are
under the jurisdiction of the Secretary of
Commerce and all other species are
under the jurisdiction of the Secretary of
the Interior. Authority to administer the
Act has been delegated by the Secretary
of the Interior to the Director of FWS
and by the Secretary of Commerce to the
Assistant Administrator for Fisheries.
There have been no comprehensive
amendments to the Act since 1988, and
no comprehensive revisions to part 424
of the implementing regulations since
1984. In the years since those changes
took place, the Services have gained
considerable experience in
implementing the critical habitat
requirements of the Act, and there have
been numerous court decisions
regarding the designation of critical
habitat.
On May 1, 2012, the Services
finalized the revised implementing
regulations related to publishing textual
descriptions of proposed and final
critical habitat boundaries in the
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Federal Register for codification in the
Code of Federal Regulations (77 FR
25611). That final rule revised 50 CFR
424.12(c) to make the process of
designating critical habitat more userfriendly for affected parties, the public
as a whole, and the Services, as well as
more efficient and cost effective. Since
the final rule became effective on May
31, 2012, the Services have continued
the publication of maps of proposed and
final critical habitat designations in the
Federal Register, but the inclusion of
any textual description of the
designation boundaries in the Federal
Register for codification in the Code of
Federal Regulations is optional. Because
we revised 50 CFR 424.12(c) separately,
we do not discuss that paragraph further
in this final rule.
On August 28, 2013, the Services
finalized revisions to the regulations for
impact analyses of critical habitat (78
FR 53058). These changes were made as
a result of the President’s February 28,
2012, Memorandum, which directed us
to take prompt steps to revise our
regulations to provide that the economic
analysis be completed and made
available for public comment at the time
of publication of a proposed rule to
designate critical habitat. These
revisions also state that the impact
analysis should focus on the
incremental effects resulting from the
designation of critical habitat. Because
we have revised 50 CFR 424.19
separately, we do not discuss that
section further in this final rule.
Summary of Comments and
Recommendations
In the proposed rule published on
May 12, 2014 (79 FR 27066), we
requested that all interested parties
submit written comments on the
proposal by July 11, 2014. We also
contacted appropriate Federal and State
agencies, scientific experts and
organizations, and other interested
parties, and invited them to comment
on the proposal. We did not receive any
requests for a public hearing. We did
receive several requests for an extension
of the public comment period, and on
June 26, 2014 (79 FR 36284), we
extended the public comment period to
October 9, 2014. All substantive
information provided during the
comment periods has either been
incorporated directly into this final
determination or addressed in the more
specific response to comments below.
General Issues
(1) Comment: Several commenters,
including several States, provided edits
to the proposed regulation.
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Our Response: We have reviewed the
edits provided and, where appropriate,
we have incorporated them into this
final regulation. The more specific
comments and edits are addressed
below.
(2) Comment: Several comments
stated that the proposed changes to the
regulation would vastly expand the area
of critical habitat designation, in direct
conflict with using the critical habitat
designation as a conservation tool.
Our Response: The proposed changes
to the regulation are not likely to vastly
expand the areas included in any
particular critical habitat designation.
Many commenters focused on the
inclusion of unoccupied areas or
perception that the proposed changes
expand the Services’ authority to
include such areas in a critical habitat
designation. Section 3(5)(A) of the Act
expressly allows for the consideration
and inclusion of unoccupied habitat in
a critical habitat designation if such
habitat is determined to be essential for
the conservation of the species.
However, the existing implementing
regulations state that such unoccupied
habitat can be considered only if a
determination is made that the
Service(s) cannot recover the species
with the inclusion of only the
‘‘geographical area presently occupied’’
by the species, which is generally
understood to refer to habitat occupied
at the time of listing (50 CFR 424.12(e)).
As discussed in the proposed rule, we
have determined that the provision is an
unnecessary and redundant limitation
on the use of an important conservation
tool. Further, we have learned from
years of implementing the critical
habitat provisions of the Act that a rigid
step-wise approach, i.e., first
designating all occupied areas that meet
the definition of ‘‘critical habitat’’
(assuming that no unoccupied habitat is
designated) and then, only if that is not
enough, designating essential
unoccupied habitat may not be the best
conservation strategy for the species and
in some circumstances may result in a
designation that is geographically larger,
but less effective as a conservation tool.
Our proposed change will allow us to
consider the inclusion of occupied and
unoccupied areas in a critical habitat
designation following any general
conservation strategy that has been
developed for the species. In some cases
(e.g., wide ranging species like the
spotted owl or lynx), we have found and
expect that we will continue to find that
the inclusion of all occupied habitat in
a designation does not support the best
conservation strategy for a species. We
expect that the concurrent evaluation of
occupied and unoccupied areas for a
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critical habitat designation will allow us
to develop more precise and deliberate
designations that can serve as more
effective conservation tools, focusing
conservation resources where needed
and minimizing unnecessary regulatory
burdens.
(3) Comment: Several commenters
including one State noted that recovery
planning and critical habitat designation
are two different processes. A
commenter also asked how the Services
will ‘‘infer’’ that unoccupied areas will
eventually become necessary for
recovery given that recovery plans do
not exist at the time of listing and when
it is not appropriate to designate
unoccupied areas that are essential for
recovery.
Our Response: While we agree that
the designation of critical habitat and
the recovery planning processes are
different and guided by two separate
provisions of the Act and implementing
regulations, the ultimate goal of
developing effective conservation tools
and measures to recover a listed species
is the same. A general draft conservation
strategy or criterion that informs the
construction of a critical habitat
designation is often developed in
consultation with staff working in
recovery planning and implementation
to ensure collaboration, consistency,
and efficiency as the Services work with
the public and partners to recover a
listed species.
We have replaced the word ‘‘infer’’
with the word ‘‘determine’’ in our
preambular discussion to be clearer. We
will determine from the record and
based on any existing conservation
strategy for the species if any
unoccupied areas are likely to become
necessary to support the species’
recovery. In order to designate
unoccupied areas, we are required by
section 3(5)(A) of the Act to determine
that such areas are essential for the
conservation of the species.
(4) Comment: Several commenters
stated that this attempt by the Services
to expand their own discretion and
authority without congressional
authorization is neither justified nor
lawful.
Our Response: The amended
regulations do not expand the Services’
discretion. Rather, they clarify the
existing process by which we designate
critical habitat based on lessons learned
over many years of implementing
critical habitat and relevant case law.
The amendments synchronize the
language in the implementing
regulations with that in the Act to
minimize confusion, and clarify the
discretion and authority that Congress
provided to the Secretaries under the
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Act. The Services are exercising their
discretion to resolve ambiguities and fill
gaps in the statutory language, and the
amended regulations are a permissible
interpretation of the statute.
(5) Comment: Several commenters
were concerned that the changes would
lead to extensive litigation because the
Services failed to establish clear,
measurable, and enforceable criteria for
what should or should not be
considered ‘‘habitat’’ for a given species,
let alone whether an area should or
should not be considered critical habitat
under the Act.
Our Response: The amended
regulations do not substantially change
the manner in which critical habitat is
designated. Rather, the amendments
primarily clarify how the Services
already have been developing critical
habitat designations. We have set forth
criteria in the final rule below. We will
also refine, to the extent practicable, and
articulate the specific criteria used for
identifying which features and areas are
essential to the conservation of a species
and the subsequent development of a
critical habitat designation for each
species (using the best scientific data
available) in the proposed and final
critical habitat rules. Our intent is to be
more transparent about how we define
the criteria and any generalized
conservation strategy that may have
been used in the development of a
critical habitat designation to provide
for a more predictable and transparent
critical habitat designation process.
(6) Comment: Several commenters
stated that the Services have misled
stakeholders and effectively failed to
provide adequate notice and
opportunity for public comment. The
comments assert that we should
withdraw our proposal, republish it
with a more accurate and clear summary
of the changes to the regulations and
their implications, and provide further
opportunity for public comment.
Our Response: The Services have not
misled stakeholders. We initially
provided a 60-day public comment
period on the proposed rule.In response
to public comments requesting an
extension, we extended the comment
period for an additional 90 days. This
followed extensive coordination and
discussion with potentially affected
Federal agencies, States, and
stakeholders and partners, as well as
formal interagency review under
Executive Order 12866. We also held
subsequent calls and extensive webinars
with many stakeholders to further
inform them about the proposed rule
and address any questions or concerns
they may have had at the time. This
satisfies the Services obligation to
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provide notice and comment under the
Act and the Administrative Procedure
Act (APA).
(7) Comment: Several tribes
commented that traditional ecological
knowledge should constitute the best
scientific data available and be used by
the Services.
Our Response: Traditional ecological
knowledge (TEK) is important and
useful information that can inform us as
to the status of a species, historical and
current trends, and threats that may be
acting on it or its habitat. The Services
have often used TEK to inform decisions
under the Act regarding listings, critical
habitat, and recovery. The Act requires
that we use the best scientific and
commercial data available to inform
decisions to list a species and the best
scientific data available to inform
designation of critical habitat, and in
some cases TEK may be the best data
available. The Services cannot
determine, as a general rule, that TEK
will be the best available data in every
rulemaking. However, we will consider
TEK along with other available data,
weighing all data appropriately in the
decision process. We will explain the
sources of data, the weight given to
various types of data, and how data are
used to inform our decision. Further,
any data, including TEK, used by the
Services to support a listing
determination or in the development of
a critical habitat designation may be
subject to disclosure under the Freedom
of Information Act (FOIA).
(8) Comment: One State strongly
advised the Services to withdraw the
Federal Register notice and form a
Policy Advisory group on the issue. The
Western Governors’ Association
requested that the rule be reworked in
cooperation with Western States and
utilize State data to reach a more legally
defensible result and to foster
partnerships.
Our Response: We appreciate the
interest by the State and Western
Governors’ Association to form a policy
advisory group and work collaboratively
with the Services. However, the
Services have already coordinated with
States, Federal agencies, and partners to
develop the amended regulations, and
do not agree that a Policy Advisory
group is necessary. The Services have
relied on input from States and other
entities, as well as lessons we have
learned from implementing the
provisions for critical habitat under the
Act, to make the regulations consistent
with the statute, codify our existing
practices, and provide greater clarity
and flexibility to designate critical
habitat so that it can be a more effective
conservation tool. We will continue
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working collaboratively with Federal,
State, and private partners to ensure that
our critical habitat designations are
based on the best available scientific
information and balance the
conservation needs of the species with
the considerations permitted under
section 4(b)(2).
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Scope and Purpose (Section 424.01)
(9) Comment: Several commenters
including several States suggested that
we retain the words ‘‘where
appropriate’’ to qualify the reference to
designation or revision of critical habitat
as it is a phrase of limiting potential.
Some commenters suggested that we
replace the words with ‘‘unless deemed
imprudent’’ to better clarify the
intention of this proposed change.
Our Response: As discussed in our
proposal, the phrase ‘‘where
appropriate’’ was misleading and
implied a greater flexibility than the
Services have regarding whether to
designate critical habitat. The Services
have the discretion not to designate
critical habitat only for species listed
prior to 1978 for which critical habitat
has not previously been designated or
where an explicit determination is made
that designation is not prudent. Based
on our experiences with designating
critical habitat, a determination that
critical habitat is not prudent is rare.
Removing the phrase ‘‘where
appropriate’’ still allows the Services to
determine that critical habitat is not
prudent for a species if such
determination is supported by the best
available scientific information.
Replacing it with the phrase ‘‘unless
deemed imprudent’’ implies that not
prudent determinations are common,
which is not our intent. Deleting ‘‘where
appropriate’’ provides the necessary
clarification concerning the discretion
the Services have in determining when
to designate critical habitat.
(10) Comment: Several commenters
suggested that we add the words ‘‘at the
appropriate time’’ in place of the words
‘‘where appropriate’’ to qualify the
reference to designation or revision of
critical habitat in § 424.01(a).
Our Response: The Services are
required under section 4(a)(3)(A) of the
Act to designate critical habitat, to the
maximum extent prudent and
determinable, at the time a species is
listed. The inclusion of the phrase ‘‘at
the appropriate time’’ and the
implication that the Services have
flexibility regarding the timing of the
designation process runs counter to the
statutory text.
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Definitions
(11) Comment: Several commenters
including one State asked us to keep the
definitions for ‘‘critical habitat,’’
‘‘endangered species,’’ ‘‘plant,’’
‘‘Secretary,’’ ‘‘State Agency,’’ and
‘‘threatened species’’ in the regulation
for the purpose of transparency and
clarity because they are core definitions
in the authorizing statute and are
important terms in the regulations.
Our Response: These terms are
defined in the Act itself, thus repeating
them verbatim in the implementing
regulations is redundant and does not
resolve any ambiguity.
(12) Comment: Several commenters
were concerned that the addition of the
phrase ‘‘i.e., the species is recovered’’ to
the definition of ‘‘conserve, conserving,
and conservation’’ to explain the point
at which the measures provided under
the Act are no longer necessary resulted
in a higher standard for conservation
than is warranted. Others commented
that the Services are implying that
conservation of critical habitat is
equated to meeting recovery goals.
Our Response: The use of ‘‘recovered’’
in the definition of ‘‘conserve,
conserving, and conservation’’ does not
introduce a new standard for
conservation. Rather, it clarifies the
existing link between conservation and
recovery. Conservation is the use of all
methods and procedures that are
necessary to bring any species to the
point at which measures provided by
the Act are no longer necessary.
Recovery is improvement in the status
of listed species to the point at which
listing is no longer appropriate. Also see
our response to comment 2.
(13) Comment: One commenter stated
that if the ‘‘i.e., the species is recovered’’
is added to the definition of ‘‘conserve,
conserving, and conservation,’’ then the
Services should also add the phrase ‘‘or
extinct’’ since these examples describe
when the action of conservation (a set
of methods and procedures) are not
necessary anymore.
Our Response: ‘‘Conserve, conserving,
and conservation’’ is defined in the Act
as to use and the use of all methods and
procedures which are necessary to bring
any endangered species or threatened
species to the point at which the
measures provided pursuant to this Act
are no longer necessary. Extinction does
not meet this definition because extinct
species have not been brought to the
point at which listing is no longer
necessary. Our regulations at § 424.11(d)
state that a species may be delisted for
one or more of the following reasons: (1)
Extinction; (2) Recovery; (3) Original
data for classification in error. Each of
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these is a separate category, and only
recovered species have reached the
recovered state contemplated by the
definition of ‘‘conserve, conserving, and
conservation.’’ (See our response to
comment 12).
(14) Comment: Several commenters
stated that proposing to define
‘‘geographical area occupied by the
species’’ is an amendment to the
definition in the Act and is illegal.
Our Response: The Act does not
define the phrase ‘‘geographical area
occupied by the species.’’ The Services
may develop, clarify, and revise
regulations implementing the provisions
of a statute, provided that our
interpretations do not conflict with or
exceed the authority provided by the
statute. Since there has been
considerable confusion as to the specific
area and scale the phrase refers to, we
find that it is important to provide a
reasonable and practicable definition for
this phrase based on what we have
learned over the many years of
implementing critical habitat under the
Act. Providing this definition will
clarify how we designate critical habitat
and which areas are considered
occupied at the time of listing.
(15) Comment: Several States
commented that the definition of
‘‘geographical area occupied by the
species’’ provides no objective criteria,
which will only lead to further
confusion and more litigation. One State
requested that we abandon the
definition. Several States offered revised
language.
Our Response: The Services are
defining the term ‘‘geographical area
occupied by the species’’ because the
phrase is found in the Act but is not
defined in the Act’s regulations, and
because there has been considerable
confusion over the proper interpretation
of the phrase. We have clearly stated
and explained the definition in our
proposal. Further, we will specify the
criteria used for identifying which
features and areas are essential to the
conservation of a species and the
subsequent development of a critical
habitat designation for each species
(using the best scientific data available)
in the proposed and final rules for a
particular critical habitat designation.
Our intent is to be more clear and
transparent about how we define the
criteria and any generalized
conservation strategy that may have
been used in the development of a
critical habitat designation to enhance
its use as a conservation tool.
(16) Comment: One State commented
that ‘‘regular or consistent use’’ is a
hallmark of a finding of occupied
habitat, and should be required by the
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‘‘geographical area occupied by the
species’’ definition, not excluded. The
State pointed to the decision in Arizona
Cattle Growers’ Ass’n v. Salazar, 606
F.3d 1160 (9th Cir. 2010), in which the
court upheld the application of the
Service’s definition of occupied habitat
for the Mexican spotted owl as ‘‘areas
that the owl uses with sufficient
regularity that it is likely to be present
during any reasonable span of time.’’
Another State similarly commented that
the use of the term ‘‘even if not used on
a regular basis’’ in the definition of
geographical area occupied by the
species will now enable the Services to
designate critical habitat within areas
infrequently used by a species.
Our Response: We respectfully
disagree with the commenter that the
definition of ‘‘geographical area
occupied by the species’’ should be
limited to only those areas in which the
use by the species is ‘‘regular or
consistent.’’ As discussed at length in
our proposal, we find that the phrase
‘‘geographical area occupied by the
species’’ should also include areas that
the species uses on an infrequent basis
such as ephemeral or migratory habitat
or habitat for a specific life-history
phase. We find that this more inclusive
interpretation is consistent with
legislative history and Arizona Cattle
Growers’ Ass’n v. Salazar, 606 F.3d
1160 (9th Cir. 2010), and congressional
intent. Additionally, based on our
experience of implementing the
provisions of critical habitat for many
years, we have found that there has been
considerable confusion and differing
interpretations of this phrase. Our intent
through the definition provided in our
proposal was to provide greater clarity
regarding how we interpret the phrase
and the general scale at which we define
occupancy. We give examples in the
rule of areas such as migratory
corridors, seasonal habitats, and habitats
used periodically (but not solely by
vagrant individuals). We will use the
best scientific data available to
determine if such areas occur for a
species. Each species’ life cycle is
different and the details of such areas,
if they exist, would be explained in the
proposed and final rules designating
critical habitat for a particular species.
These areas would also have to meet the
criteria for occupied areas in the
definition of critical habitat found in the
Act.
(17) Comment: One commenter stated
that the definition of ‘‘geographical area
occupied by the species’’ fails to include
paragraph 3(5)(C) from the Act: ‘‘Except
in those circumstances determined by
the Secretary, critical habitat shall not
include the entire geographical area
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which can be occupied by the
threatened or endangered species.’’
Our Response: The regulatory
definition is intended to clarify how we
interpret the phrase, not to repeat the
language of the statute. Further,
paragraph 3(5)(C) in the Act, applies to
the geographic area that can be
occupied by a species, as opposed to the
geographic area actually occupied by
the species.
(18) Comment: Several commenters
including several States stated that the
definition of ‘‘geographical area
occupied by the species’’ provides
unlimited discretion and authority to
the Secretary to determine the
boundaries and size of the critical
habitat area.
Our Response: While we agree that
the Secretaries are afforded significant
discretion and authority to define and
designate critical habitat, we
respectfully disagree with the
commenter that the discretion and
authority is unlimited. First, critical
habitat is to be defined and designated
based on the best scientific data
available. Second, we have learned from
years of implementing the critical
habitat provisions of the Act that often
a rigid step-wise approach, i.e., first
designating all occupied areas that meet
the definition of ‘‘critical habitat’’
(assuming that no unoccupied habitat is
designated) and then, only if that is not
enough, designating essential
unoccupied habitat, may not be the best
conservation strategy for the species and
in some circumstances may result in a
designation that is geographically larger,
but less effective as a conservation tool.
By providing a definition of
‘‘geographical areas occupied by the
species’’ along with the other revisions
and clarifications in our proposal, we
can be more precise and deliberate in
the development of our critical habitat
designations following any general
conservation strategy that has been
developed for the species. Lastly, we are
still bound by paragraph 3(5)(C) (see
response to Comment 17 above).
(19) Comment: Several commenters
asked, ‘‘What standards will be in place
to substantiate that such areas are used
as part of a species’ life cycle and not
just an individual vagrant’s life cycle’’
in the definition of ‘‘geographical area
occupied by the species.’’ Several States
also commented that the vagrant animal
exception in the rule is vague and
subject to varying interpretations
because no definition of ‘‘vagrant’’ is
provided.
Our Response: As stated in our
proposed rule, vagrant individuals are
species who wander far from the known
range of the species. We will use the
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best scientific data available to
determine whether an area is used by a
species for part of its life cycle versus
an individual vagrant’s life cycle. The
basis for our determination on this point
will be articulated in our proposed and
final rules designating critical habitat
for a particular species and subject to
public review and comments, as well as
peer review.
(20) Comment: Several commenters
suggested that we add the word
‘‘regularly’’ to the sentence ‘‘Such areas
may include those areas used regularly
throughout all or part of the species’ life
cycle’’ in the definition of ‘‘geographical
area occupied by the species.’’
Our Response: The suggested addition
would conflict with the second part of
the sentence, in which we state ‘‘even
if not used on a regular basis (e.g.,
migratory corridors, seasonal habitats,
and habitats used periodically, but not
solely by vagrant individuals).’’ If the
best scientific data available indicates
that these areas are used periodically
during some portion of the listed
species’ life history, then these areas
should be considered in the
development of a critical habitat
designation.
(21) Comment: Several commenters
questioned what would happen to the
size, shape, and location of critical
habitat areas that were designated in
areas that were not regularly used as
conditions change and travel corridors
shift or breeding areas move.
Our Response: As discussed in our
proposal and throughout this final rule,
critical habitat is to be based on the best
scientific data available, and to the
maximum extent prudent and
determinable promulgated concurrent
with the listing of a species. Often at the
time of listing when we are developing
a designation of critical habitat for a
species, we may have only limited data
concerning the distribution of the
species, its life-history requirements,
and other factors that can inform the
identification of features or specific
areas essential to the conservation of the
species. Such limited data may still be
the best scientific data available. The
Services are required in a proposed and
final designation of critical habitat to
clearly articulate what data are being
used and the criteria for defining the
specific essential features and areas. The
Services must also allow for public
review and comments on the proposal
to ensure public involvement in the
process and provide as much clarity and
transparency as possible. The
designation of critical habitat results in
a regulation in which the boundaries of
critical habitat for a species are defined.
These boundaries can be changed only
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through rulemaking. Thus, if habitat
changes following a designation, such
that those specific areas no longer meet
the definition of ‘‘critical habitat,’’ the
areas within the boundaries of critical
habitat are still critical habitat until
such time as a revision to the
designation is promulgated. Any
interested party may file a petition with
the Services to request revision of a
critical habitat designation.
(22) Comment: A number of
commenters, including several States,
asserted that the proposed definition of
‘‘geographical area occupied by the
species’’ is so vague it could lead to
huge areas of unoccupied and
potentially unsuitable habitat being
designated as critical habitat that would
result in the public or the regulated
community having no consistency.
Our Response: The proposed
definition would not lead to more
expansive critical habitat designations.
We do not designate areas that are
occupied at the time of listing unless
those areas have one or more of the
physical or biological features present
that are essential to the conservation of
the species and may require special
management considerations or
protection. Any unoccupied habitat at
the time of listing could only be
designated critical habitat under section
3(5)(A)(ii) of the Act, which requires a
determination by the Secretary that such
areas are essential for the conservation
of the species. Further, we will
articulate the specific criteria used for
identifying which features and areas are
essential to the conservation of a species
during the subsequent development of a
critical habitat designation for each
species (using the best scientific data
available) in the proposed and final
rules designating critical habitat for that
species. Our intent is to be more clear
and transparent about how we define
the criteria for designation and how in
the development of a critical habitat
designation we use any generalized
conservation strategy that may have
been developed for the species. The
proposed rule would inform the public,
including landowners and businesses,
of our critical habitat designation and
allow them time to review and provide
comments.
(23) Comment: Two States
commented that the Services have
justified the new definition of
‘‘geographical area occupied by the
species’’ by misrepresenting the court’s
decision in Otay Mesa Property L.P. v.
DOI, 646 F.3d 914 (D.C. Cir. 2011),
reversing 714 F. Supp. 2d 73 (D.D.C.
2010). The States contend that we
asserted that the D.C. Circuit’s decision
supported our interpretation, even
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though a thorough review of the
decision reveals the court did not hold
or find that the Act allows the Services
to make a post-listing determination of
occupancy if based on adequate data,
simply because the court did not decide
that particular issue.
Our Response: We agree that the D.C.
Circuit did not hold or find that the ESA
allows the Services to make a postlisting determination of occupancy. Our
proposed rule, however, did not assert
that the circuit court opinion supported
our interpretation. Instead, the proposed
rule correctly noted that the district
court opinion supported our
interpretation. See 714 F. Supp. 2d at 83
(‘‘The question, therefore, is not
whether FWS knew in 1997, when it
listed the San Diego fairy shrimp as
endangered, that there were San Diego
fairy shrimp on Plaintiffs’ property but,
rather, whether FWS reasonably
concluded, based on data from 2001,
that the shrimp had been on the
property in 1997.’’). Because that
decision was reversed by the D.C.
Circuit, however, we needed to explain
what effect that D.C. Circuit’s decision
had on the district court opinion with
respect to this issue. Because the D.C.
Circuit reversed the district court’s
opinion on other grounds (i.e., that the
evidence in the record was inadequate),
the D.C. Circuit did not address the
interpretive issue of whether later data
can support a determination of
occupancy at the time of listing. Thus,
we stated, accurately, that the D.C.
Circuit ‘‘did not disagree’’ with this
aspect of the district court’s opinion. We
did not mean to suggest that the D.C.
Circuit had considered and affirmed this
aspect of the district court’s opinion.
(24) Comment: One State commented
that the Service’s reliance on the
decision in Arizona Cattle Growers’
Assoc. v. Salazar, 606 F.3d 1160 (9th
Cir. 2010), to expand the definition of
‘‘occupied’’ is misplaced because the
Services oversimplify and misstate the
court’s ruling. The State provided
additional detail regarding the court’s
analysis, noting a variety of factors that
the court suggested were relevant to a
case-by-case determination of
occupancy, and the court’s emphasis on
reasonableness.
Our Response: None of the detail
provided by the State is inconsistent
with our summary of the holding: ‘‘a
determination that a species was likely
to be temporarily present in the areas
designated as critical habitat was a
sufficient basis for determining those
areas to be occupied, even if the species
was not continuously present.’’
(25) Comment: One commenter
asserted that the ‘‘physical or biological
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features’’ definition has too many if and
if/then scenarios that appear too
scientifically attenuated to serve as an
appropriate basis for critical habitat
designations.
Our Response: In defining physical
and biological features, we provided
examples of types of features and
conditions that we have found to be
essential to certain species based on
experience over many years of
designating critical habitat for a wide
variety of species. The determination of
specific features essential to the
conservation of a particular species will
be based on the best scientific data
available and explained in the proposal
to designate critical habitat for that
species, which will be available for
public comment and peer review.
(26) Comment: Several States
commented that the new definition of
‘‘physical or biological features’’ is
excessively broad and completely
unnecessary. They stated that the new
definition goes too far and allows the
Services to include areas that do not
currently have any essential physical or
biological features necessary for a
species; they asserted that the original
language of the Act provides enough
latitude to allow for ephemeral,
essential habitat requirements. Two
States also asked the Services to more
clearly define the phrase ‘‘reasonable
expectation’’ found in the preamble
discussion (‘‘the Services could
conclude that essential physical or
biological features exist in a specific
area . . . if there were documented
occurrences of the particular habitat
type in the area and a reasonable
expectation of that habitat occurring
again’’).
Our Response: Because the term
‘‘physical or biological features’’ is not
defined in the Act, the Services clarify
how they have been using this term. A
‘‘reasonable expectation’’ would be
based on the best scientific data
available showing that the habitat has a
temporal or cyclical nature in that in
some years particular habitat elements
may not be present, but the record
indicates that, once certain conditions
are met, the habitat will recur and be
used by the species.
(27) Comment: One State contended
that the Services support the new
definition of ‘‘physical or biological
features’’ with a flawed interpretation of
the opinion in Cape Hatteras Access
Preservation Alliance v. DOI, 344 F.
Supp. 2d 108 (D.D.C. 2004). According
to the State: That opinion does not
justify expanding the meaning and
breadth of the phrase; the Services
should withdraw the definition because
the Services cite no authority for making
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such a change and thus lack any
justification for doing so; the Court
explicitly rejected the Service’s attempt
to broaden the scope of critical habitat
designation; and the Services should not
attempt to expand their authority by
circumventing the Federal courts.
Our Response: The district court
rejected the U.S. Fish and Wildlife
Service’s critical habitat designation for
the piping plover as including lands
that did not currently contain the
features defined in the rule, but noted
that it was not addressing whether
dynamic land capable of supporting
plover habitat can itself be one of the
physical or biological features essential
to the conservation of the plover. The
court noted that the Service had not
made that assertion in the context of the
piping plover designation. To address
this unintentional gap, we are setting
out our interpretation as part of the
framework regulations. This new
definition clarifies that features can be
dynamic or ephemeral habitat
characteristics. We clearly state in the
rule that an area within the geographical
area occupied by the species, with
habitat that is not ephemeral by nature
but that has been degraded in some way,
must have one or more of the features
at the time of designation to be critical
habitat.
(28) Comment: Several commenters
recommended that the Services
separately define ‘‘physical features’’
and ‘‘biological features’’ to provide
greater clarity.
Our Response: The Act refers to
‘‘physical or biological features,’’ so it is
not necessary to define them separately.
We find that the definition provided in
the draft proposal along with the
examples and accompanying
explanation provides sufficient clarity
and that separately defining these terms
in the final regulation would not be
helpful. However, the Services must
clearly articulate, in proposed and final
rules designating critical habitat for a
particular species, which physical or
biological features are essential to the
conservation of the species and the basis
for that critical habitat.
(29) Comment: Several commenters
suggested that we remove ‘‘at a scale
determined by the Secretary to be
appropriate’’ and add ‘‘for a specific
unoccupied area to be designated as
critical habitat, it must be reasonably
foreseeable that (1) such area will
develop the physical and biological
features necessary for the species and
(2) such features will be developed in an
amount and quality that the specific
area will serve an essential role in the
conservation of the species.’’
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Our Response: We determine whether
unoccupied areas are essential for the
conservation of the species by
considering the best available scientific
data regarding the life-history, status,
and conservation needs of the species,
which include considerations similar to
those raised by the commenter.
However, we do not agree that the
specific findings suggested by the
commenter either are required under the
statute or are useful limitations for the
Services to impose on themselves.
Further, our rationale for why
unoccupied areas are essential for the
conservation of the species will be
articulated in the proposed rule
designating critical habitat for a
particular species and available for
public review and comment. Finally, we
decline to remove the language ‘‘at a
scale determined by the Secretary to be
appropriate because we have concluded
that it is useful to clarify that different
circumstances will require different
scales of analysis, and the Secretary
retains the discretion to choose an
appropriate scale.
(30) Comment: A commenter
suggested that we add the phrase ‘‘based
on the best scientific data available’’
after the word ‘‘appropriate’’ in ‘‘the
Secretary will identify, at a scale
determined by the Secretary to be
appropriate’’ in § 424.12(b)(2). The
commenter further stated that this
provides a reference to the scientific
basis on which the Secretary will
determine this scale.
Our Response: The phrase ‘‘based on
the best scientific data available’’ is
captured in § 424.12(b)(1)(ii). Under
section 4(b)(2) of the statute, it also
states that the Secretary shall designate
critical habitat, and make revisions
thereto, under subsection (a)(3) on the
basis of the best scientific data available.
It would be redundant to add the phrase
to the section the commenter has
suggested. Nevertheless, as stated above,
the Secretary’s choice of scale will be
based on the best available scientific
data.
(31) Comment: A commenter
suggested that we replace the phrase
‘‘conservation needs of the species’’
with ‘‘physical or biological features’’ in
§ 424.12(b)(2). The commenter stated
that the phrase ‘‘conservation needs of
the species’’ is undefined and adds
ambiguity to the regulation.
Our Response: Section 424.12(b)(2)
refers to the designation of critical
habitat in unoccupied areas. Under
section 3(5)(A)(ii) of the statute,
unoccupied areas are subject only to the
requirement that the Secretary
determine that such areas are essential
for the conservation of the species. The
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presence of physical or biological
features is not required by the statute for
the inclusion of unoccupied areas in a
designation of critical habitat.
Incorporating the edit suggested by the
commenter would limit Secretarial
discretion in a way inconsistent with
the statute by mandating the presence of
essential features as a prerequisite to
inclusion of unoccupied areas in a
critical habitat designation. Therefore, it
would be inappropriate to use the term
‘‘physical or biological features’’ in this
section.
(32) Comment: Several commenters
stated that the Services’ claim that they
may designate acres or even square
miles without evidence that those areas
contain features essential to the
conservation of the species is contrary
to the Act. Two States commented that
the scale of critical habitat should not be
left to the Secretary’s absolute discretion
and must be chosen and justified at a
scale that both makes sense in terms of
the habitat needs of the species and is
fine enough to demonstrate that the
physical or biological features are found
in each specific area of occupied
habitat. One State also provided revised
language for § 424.12(b)(1) by replacing
‘‘at a scale determined by the Secretary
to be appropriate’’ with ‘‘at a scale
consistent with the geographical extent
of the physical or biological features
essential to the species’ conservation.’’
Our Response: We state in the
proposed regulation that the Secretary
need not determine that each square
inch, yard, acre, or even mile
independently meets the definition of
critical habitat. However, setting out
defined guidelines for the scale of an
analysis in regulations would not be
practicable for the consideration of
highly diverse biological systems and
greatly differing available data. Each
critical habitat designation is different
in terms of area proposed, the
conservation needs of the species, the
scope of the applicable Federal actions,
economic activity, and the scales for
which data are available. Additionally,
the scale of the analysis is very fact
specific. Therefore, the Services must
have flexibility to evaluate these
different areas in whatever way is most
biologically and scientifically
meaningful. For example, for a narrowendemic species, a critical habitat
proposal may cover a small area; in
contrast, for a wide-ranging species, a
critical habitat proposal may cover an
area that is orders of magnitude greater.
The appropriate scale for these two
species may not be the same. For the
narrow-endemic species, we may look at
a very fine scale with a great level of
detail. In contrast, for the wide-ranging
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species, which may cover wide
expanses of land or water, we may use
a coarser scale, due to the sheer size of
the proposed designation. Each critical
habitat proposal includes a description
of the scope of the area being proposed,
and uses a scale appropriate to that
situation based on the best scientific
data available. The suggested language
would not allow for the Secretarial
discretion that is needed to be flexible
to meet the conservation needs of the
species. The proposed rule designating
critical habitat for a particular species is
made available for public review and
comment, and interested parties may
comment on the scale for a specific
designation.
(33) Comment: Several commenters
stated that, in reaching this
determination, the Services appear to
conflate disparate terminology (specific
areas versus occurrences) and rely upon
a vague term (range) that does not
adequately delineate what geographic
areas are actually occupied by a species.
Several commenters also requested
additional explanation of the term
‘‘range.’’
Our Response: Under section
3(5)(A)(i) of the Act, specific areas
designated as critical habitat include
those specific areas within the
geographical area occupied by the
species at the time the species is listed.
As discussed in our proposal and this
final rule, the geographical area that
may generally be delineated around the
species’ occurrences is synonymous
with the species’ range. The term
‘‘range’’ used in our proposal refers to
the general area currently occupied by
the species at the time the listing
determination is made. These areas are
occupied by the species throughout all
or part of the species’ life cycle, even if
not used on a regular basis. Some
examples we give are migratory
corridors, seasonal habitats, and habitats
used periodically, but not solely by
vagrant individuals. This scale of
occupancy is different from a very
narrow or limited delineation of areas of
occupancy identified through presence
and absence surveys for localized
occurrences of the species. We,
therefore, disagree that we are using a
vague term in referring to range.
(34) Comment: Several commenters
including one State stated that by
defining the geographical area occupied
by the species as coextensive with the
‘‘range’’ and including multiple areas of
occurrence, the Services are expanding
the geographic extent of occupied
habitat beyond the limits of judicial
interpretation. They suggested we
should define the area occupied by the
species as limited to the specific
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location where the species occurs on a
regular or consistent basis.
Our Response: We have indicated that
the geographical area occupied by the
species is likely to be larger than the
specific areas that would then be
analyzed for potential designation under
section 3(5)(A)(i). We are not suggesting
that the specific areas included in
critical habitat should fill this area. To
limit the definition to specific locations
where the species occurs on a regular or
consistent basis would not allow the
Secretaries to designate areas that may
be important for the conservation of a
listed species that may only be
periodically used by a species, such as
breeding areas, foraging areas, and
migratory corridors, thereby limiting
Secretarial discretion.
(35) Comment: One State asked if the
range in the geographical area occupied
by the species definition refers to the
historical range or the currently
occupied range.
Our Response: The term ‘‘range’’ as
indicated in our proposal refers to the
generalized area currently occupied by
the species at the time the listing
determination is made, not the
historical range.
(36) Comment: One State also wanted
to know if land-use restrictions within
the geographical area occupied by the
species would be put into place in
addition to the designated critical
habitat.
Our Response: The revised
regulations would not result in any
change to land-use restrictions beyond
the existing regulatory requirements
under section 7 of the Act that Federal
agencies consult with the Services to
ensure that the actions they carry out,
fund, or authorize are not likely to
destroy or adversely modify critical
habitat (see the final rule published
elsewhere in today’s Federal Register).
The Act provides no special regulatory
protections for those areas within the
geographic area occupied by the species
that are not designated as critical
habitat, although the section 7
prohibition on jeopardy and the section
9 prohibitions may still be applicable.
(37) Comment: Several States disagree
with the Services’ interpretation of the
definition of ‘‘occupied.’’ This
interpretation and inclusion of
‘‘periodic or temporary’’ areas will lead
to a much larger consideration of critical
habitat that is largely unnecessary for
species recovery.
Our Response: Identifying the
geographic area occupied at the time of
listing is only the first step in
designating critical habitat. In occupied
areas, we can only designate critical
habitat if one or more of the physical or
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biological features are present and are
found to be essential to the conservation
of the species and may require special
management considerations or
protection. The inclusion of periodic or
temporary areas would be based on the
best scientific data available for the
species and these areas would have to
meet the criteria above.
(38) Comment: Several commenters
asked what constitutes being
‘‘temporarily present?’’ The Services
should explain that occupied areas
require a demonstration of regular or
consistent use within a reasonable
period of time. One State commented
that the Services should clarify the
meaning of the terms ‘‘periodically’’ and
‘‘temporarily’’ to provide adequate
guidance and set reasonable limits for
potential critical habitat designations.
Our Response: We will use the best
scientific data available to determine
occupied areas including those that are
used only periodically or temporarily by
a listed species during some portion of
its life history. This will be determined
on a species-by-species basis, and our
rationale would be explained in the
proposed and final rules for these
species, which would be available for
public review and comment.
(39) Comment: Several commenters,
including two States, were concerned
about using ‘‘indirect or circumstantial’’
evidence to determine occupancy and
questioned whether this qualified as the
best scientific data available. One of the
commenters asserted that the Services
should only designate areas as occupied
based on scientific evidence (including
traditional and local knowledge) that
breeding, foraging, or migratory
behaviors actually occur in that location
on a regular or consistent basis.
Our Response: The Services will rely
on the best scientific data available in
determining which specific areas were
occupied at the time of listing and
which of these contain the features
essential to the conservation of the
species. The best available scientific
data in some cases may only be indirect
or circumstantial evidence. We will
explain in the proposed rule designating
critical habitat for a particular species if
and how such evidence was used to
determine occupancy and will provide
the public with an opportunity to
review and comment.
(40) Comment: Several commenters,
including two States, asked us to define
and explain ‘‘life-history needs.’’
Our Response: We give a sample list
of life-history needs in the rule. This list
includes but is not limited to water
characteristics, soil type, geological
features, sites, prey, vegetation,
symbiotic species, or other features. The
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life-history needs are what the species
needs throughout its different life stages
to survive and thrive.
(41) Comment: One State commented
that the term ‘‘sites’’ in the definition of
‘‘physical or biological features’’ is
wholly ambiguous and must be defined,
explained, or deleted.
Our Response: We included the term
‘‘sites’’ in the definition of physical or
biological features to keep the same
level of specificity as currently is called
for in the regulations, and our current
regulations list ‘‘sites for breeding,
reproduction, rearing of offspring,
germination, or seed dispersal’’ among
the examples of primary constituent
elements that might be specified (50
CFR 424.12(b)(4)). The term ‘‘sites’’ does
not need to be defined or further
explained because we rely on a plain
dictionary meaning of ‘‘site’’: The place,
scene, or point of an occurrence or event
(Merriam-Webster, 2015).
(42) Comment: One State suggested
that we simplify the ‘‘physical or
biological features’’ definition as
follows: ‘‘Geographic or ecological
elements within a species’ range that are
essential to its survival and
reproduction, whether single or in
combination, or necessary to support
ephemeral habitats. Features may be
described in conservation biology terms,
including patch size and connectivity.’’
Our Response: We appreciate the
State providing edits to simplify the
phrase; however, based on our years of
experience designating critical habitat
and implementing it, we find that the
text in our proposal and this final rule
will provide greater clarity.
(43) Comment: Several commenters,
including one State, indicated that we
needed a more specific delineation of
what features may be considered and
how they relate to the needs of the
species.
Our Response: We respectfully
disagree with the commenters that
further clarification should be added in
this revised regulation. However, we do
agree that we need to clearly articulate
in our proposed and final rules
designating critical habitat for each
species how the essential features relate
to the life-history and conservation
needs of the species. This type of
specificity will be in the individual
proposed and final rules designating
critical habitat for each species. As is
our general practice, we will clearly lay
out the features and how they relate to
the needs of the species in each rule.
(44) Comment: Several commenters
asked us to clarify the distinction, if
any, between features that support the
life-history needs of the species and
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features that are essential to the
conservation of the species.
Our Response: Our definition of
physical or biological features is the first
step, and we do not assume that all
features are essential. In many
circumstances the features that support
life-history needs of the species are the
features that are essential to the
conservation of the species. The features
that are essential to the conservation of
the species are those found in the
appropriate quality, quantity, and
spatial and temporal arrangements in
the context of the life history, status,
and conservation needs of the species.
This varies according to the species. For
example, for a small, endemic species
the features that support the life-history
needs may be essential themselves, but
for a wide-ranging species what rises to
the level of essential features may rely
more on the quality, quantity, and
arrangement of those features.
(45) Comment: Several commenters
sought an explanation for how the
requisite physical and biological
features would be identified,
documented, and verified during the
critical-habitat-designation process.
Our Response: We use the best
scientific data available to determine the
life-history needs of the species. The
essential physical or biological features
support the life-history and
conservation needs of the species. A
description of the essential features for
each species and how they relate to its
life-history and conservation needs will
be articulated in the proposed and final
rules designating critical habitat for a
particular species. This description of
the essential features, as well as the
designation that is based on them, will
be available for public review and
comment during the rulemaking
process.
(46) Comment: Several commenters
stated that the description of the
relevant features cannot be in broad
terms, but must be specific enough to
limit critical habitat to the most
‘‘essential areas’’ and help provide an
understanding of what the species
actually requires to return from the
brink of extinction.
Our Response: When evaluating
occupied habitat, we agree that the
statute requires us to determine which
areas contain physical or biological
features essential to the conservation of
the species (that may require special
management considerations or
protection). In every proposed and final
rule designating critical habitat for a
particular species, we describe those
features that we have determined to be
essential and explain the basis for our
determination. However, we
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respectfully disagree that broadly
described features are necessarily
inappropriate. The level of specificity in
our description of the features is
primarily determined by the state of the
best scientific information available for
that species. We will provide as much
specificity as is appropriate in light of
what is known about the species’ habitat
needs, while recognizing that the
available science may still be evolving
for that species. Where the available
information is still evolving, it may not
be possible or necessary to provide a
high level of specificity, and it may
frustrate the conservation purposes of
the Act to attempt to do so. See Arizona
Cattle Growers’ Ass’n v. Kempthorne,
534 F. Supp. 2d 1013, 1025 n.2 (D. Ariz.
2008), aff’d sub nom. Arizona Cattle
Growers’ Ass’n v. Salazar, 606 F.3d
1160 (9th Cir. 2010).
Finally, we must disagree with the
commenter’s suggestion that in
identifying essential features the
Services must identify what the species’
actually requires to return from ‘‘the
brink of extinction.’’ Critical habitat is
generally required for threatened
species as well as endangered species.
Moreover, the Services are not required
to have developed a recovery plan prior
to designating critical habitat for any
species. Home Builders Ass’n of
Northern Cal. v. U.S. Fish and Wildlife
Service, 616 F.3d 983, 989–90 (9th Cir.
2010). Our determinations of which
features are ‘‘essential’’ thus depend on
an understanding of the species’ habitat
needs rather than on a specific
projection of how the species could be
recovered.
(47) Comment: Several commenters
stated that the plain language of the Act
limits the scope of any designated area
to those features essential to the species,
and does not authorize the designation
of areas that may include those
subsidiary characteristics that are
essential for the development of the
features themselves.
Our Response: We respectfully
disagree and interpret the statutory
language not to limit ‘‘features’’ to those
habitat characteristics that make habitat
immediately usable by the species. In
other words, the physical or biological
features referred to in the definition of
‘‘critical habitat’’ can include features
that allow for the periodic development
of habitat characteristics immediately
usable by the species. An interpretation
of ‘‘features’’ that referred only to
immediately usable habitat would
render many essential areas ineligible
for designation as critical habitat,
thwarting Congress’s intent that
designation of critical habitat should
contribute to species’ conservation.
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We will use the best scientific data
available to identify features essential to
the conservation of the species and
clearly identify how they relate to the
life-history and conservation needs of
the species. When considering what
features are essential, it is sometimes
necessary to allow for the dynamic
nature of the habitat, such as
successional stages of habitat, which
could consist of old-growth habitat or
habitat newly formed through
disturbance events such as fire or flood
events. Thus, the physical or biological
features essential to the conservation of
the species may include features that
support the occurrence of ephemeral or
dynamic habitat conditions. The
example we gave in the proposed rule
was a species that may require earlysuccessional riparian vegetation in the
Southwest to breed or feed. Such
vegetation may exist only 5 to 15 years
after a local flooding event. The
necessary features, then, may include
not only the suitable vegetation itself,
but also the flooding events,
topography, soil type, and flow regime,
or a combination of these characteristics
and the necessary amount of the
characteristics that can result in the
periodic occurrence of the suitable
vegetation. The flooding event would
not be a subsidiary characteristic as
suggested by the commenter, but would
itself be a feature necessary for the
vegetation to return. So in this case, it
would be a combination of features,
flooding, and vegetation that would be
necessary to the conservation of the
species.
(48) Comment: Several commenters,
including two States, were concerned
that designating critical habitat based on
the presence of certain characteristics
that may be necessary to eventually
support the periodic occurrence of
riparian vegetation, without evidence
that the vegetation would actually
develop, constitutes an impermissible
reliance upon hope and speculation.
They further stated that the Services
must go through a separate inquiry
determining why it is reasonably
foreseeable to conclude that the
potential critical habitat will develop
the physical or biological features at
some point in the future.
Our Response: We will use the best
scientific data available to support the
identification of features essential to the
conservation of the species and clearly
identify how they relate to the lifehistory and conservation needs of the
species. When considering what
features are essential, it is sometimes
necessary to allow for the dynamic
nature of the habitat, such as
successional stages of habitat, which
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could consist of old-growth habitat or
habitat newly formed through
disturbance events such as fire or flood
events. This does not constitute reliance
on mere hope or speculation but is
based on an understanding of the
relevant ecological processes. We also
disagree with the characterization of
this situation as involving ‘‘potential
critical habitat’’ that ‘‘will develop the
physical or biological features at some
point in the future.’’ Properly
understood, the essential features would
currently exist in these areas, even
though they may not be currently
manifesting the shorter-term habitat
conditions immediately usable by the
species. Such areas may currently meet
the definition of ‘‘critical habitat’’ and
not be merely ‘‘potential critical
habitat.’’
(49) Comment: Several commenters
stated that the Services’ position that
‘‘most circumstances’’ require ‘‘special
management’’ is inconsistent with
congressional intent to narrow the
definition of ‘‘critical habitat’’ to require
a very careful analysis of what is
actually needed for survival of the
species. Several commenters, including
two States, also indicated that the
Services must continue to make the
factual determination that special
management is needed as required by
the Act.
Our Response: We make the
determination and describe the special
management considerations or
protections that may be needed in the
proposed and final rules designating
critical habitat for each critical habitat
area. However, it has been our
experience that, in most circumstances,
the physical or biological features
essential to the conservation of
endangered species may require special
management considerations or
protection in all areas in which they
occur. This is particularly true for
species that have significant habitatbased threats, which is the case for most
of our listed species. The statute directs
us to identify the essential physical or
biological features which ‘‘may require’’
special management considerations or
protection, a standard that suggests we
should be cautious and protective. We
do acknowledge that if in some areas the
essential features clearly do not require
special management considerations or
protection, then that area does not meet
this part (section 3(5)(A)(i)) of the
definition of ‘‘critical habitat.’’
However, we expect based on our
experience with designating critical
habitat that these circumstances will be
rare. In our proposed and final critical
habitat rules, we will continue to make
factual determinations as to whether
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special management considerations or
protection may be required.
(50) Comment: Several States
commented that the new interpretation
of ‘‘special management considerations
or protection’’ set out in the preamble
appears to presume that areas covered
by existing protection plans will
actually be more likely to be designated
as critical habitat, and could act as a
disincentive to implementing voluntary
pre-designation conservation initiatives,
in direct contravention to recent
Services’ policies attempting to
incentivize voluntary conservation.
Our Response: We respectfully
disagree. We are directed by the Act to
identify areas that meet the definition of
‘‘critical habitat’’ (i.e., occupied areas
that contain the essential physical or
biological features that may require
special management considerations or
protection and unoccupied areas that
are essential for the conservation of a
species) without regard to land
ownership. We also make the
determination and describe the special
management considerations or
protections that may be needed in the
proposed and final rules for each critical
habitat area. The consideration of
whether features in an area may require
special management considerations or
protection occurs independent of
whether any form of management or
protection occurs in the area. This does
not preclude the Services from
considering the exclusion of these areas
under section 4(b)(2) of the Act based on
conservation programs, plans, and
partnerships prior to issuing the final
critical habitat rule.
(51) Comment: Several commenters
stated that the Services cannot designate
critical habitat based on the general
assertions that the area contains the
essential physical or biological features.
Instead, the Services must demonstrate
that the relevant features are found
within a specific area.
Our Response: In the first part of the
definition of ‘‘critical habitat’’ in the
Act, we are required to identify specific
areas within the geographical area
occupied by the species at the time it is
listed on which are found those
physical or biological features essential
to the conservation of the species and
which may require special management
considerations or protection. In our
proposed and final critical habitat rules,
we identify which features occur in the
area, the basis on which we are
identifying them as essential features,
including how they provide for the lifehistory and conservation needs of the
species, and whether they may require
special management considerations or
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protection. These rules will be available
for public review and comment.
(52) Comment: Several commenters
suggested that we remove ‘‘principles of
conservation biology’’ from the
definition of ‘‘physical and biological
features.’’
Our Response: We respectfully
disagree. The sentence ‘‘Features may
also be expressed in terms of relating to
principles of conservation biology, such
as patch size, distribution distances, and
connectivity’’ explains more clearly
how we may identify the features. The
principles of conservation biology are
generally accepted among the scientific
community and consistently used in
species-at-risk status assessments and
development of conservation measures
and programs.
(53) Comment: Several commenters
requested that we add language
delineating the area ‘‘around’’ the
species occurrences, either by using a
distance or a reference to the species’
natural functions in the geographic area
definition.
Our Response: We are unable to
determine a universal distance or a
reference to the species’ natural
functions that would be applicable to all
species. This analysis and
determination is best left to the specific
critical habitat rulemaking for a given
species. In those proposed and final
rules, we can be specific for each
species based on its life-history needs
and more precisely define the
geographical area occupied by the
species. The rules will be available for
public review and comment.
(54) Comment: Several commenters,
including one State, indicated that the
proposed § 424.12(b)(2) and deletion of
current § 424.12(e) would relieve the
Services of any requirements that they
justify the designation of unoccupied
habitat by demonstrating the
inadequacies of occupied habitat for the
conservation of the species. They
further stated that this was a major
departure in the law regarding
designation of critical habitat.
Our Response: We respectfully
disagree. The proposed rule clearly
explains that the Act does not require
the Services to first prove that the
occupied areas are insufficient before
considering unoccupied areas. The
regulatory provision at 424.12(e) merely
restated the requirement from the
statutory definition in a different way.
We will still explain based on the best
scientific data available, why the
unoccupied areas are essential for the
conservation of the species.
(55) Comment: Several commenters
pointed out that we use ‘‘no longer
necessary’’ in the new definition of
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‘‘conserve, conserving, and
conservation’’ and the words ‘‘no longer
appropriate’’ in the definition of
‘‘recovery’’ in 50 CFR 402.02. The
commenters asserted that these are two
different standards and that we should
pick one of them.
Our Response: The words ‘‘no longer
necessary’’ are used in the statutory
definition of ‘‘conserve, conserving, and
conservation’’ in the Act. The rule
simply points out that the concept
described in the statutory language is
equivalent to ‘‘recovery.’’ That term is
defined in § 402.02, which we are not
revising at this time.
(56) Comment: Several commenters
stated that the National Marine
Fisheries Service’s interpretation of the
phrase ‘‘which interbreeds when
mature’’ was upheld by the Ninth
Circuit in Modesto Irr. Dist. v. Gutierrez,
619 F.3d 1024 (9th Cir. 2010), and that
the Act also requires that a group of
organisms must interbreed when mature
to qualify as a distinct population
segment (DPS), which is in contrast to
the Services’ interpretation of the phrase
in the proposed rule.
Our Response: We respectfully
disagree that our interpretation of
‘‘interbreeds when mature’’ is at odds
with the ruling in Modesto Irrigation
District. In that case, the Ninth Circuit
did not hold that actual interbreeding
among different populations is required
in order to include such populations in
a single DPS. To the contrary, the court
made it clear that Congress did not
intend to create a ‘‘rigid limitation’’ on
the Services’ discretion to define DPSs.
On the ‘‘narrow issue’’ of whether the
ESA or the DPS Policy required that
NMFS place interbreeding steelhead
and rainbow trout in the same DPS, the
court deferred to NMFS’s judgment that
there was no such requirement. Id. at
1037. While NMFS did state in the
challenged rule that ‘‘[t]he ESA
requirement that a group of organisms
must interbreed when mature to qualify
as a DPS is a necessary but not exclusive
condition’’ (71 FR 834, 838 (Jan. 5,
2006)), nothing in the rule suggested
that NMFS’s position was that actual
interbreeding among disparate
populations was required, and that
biological capacity to interbreed would
not be sufficient.
(57) Comment: Several commenters
stated that the Services did in fact revise
the regulations in our discussion of
‘‘interbreeds when mature’’ by inserting
the phrase ‘‘A distinct population
segment ‘‘interbreeds when mature’’
when it consists of members of the same
species or subspecies in the wild that
are capable of interbreeding when
mature’’ to the definition of a ‘‘species.’’
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They further stated that this was an
Administrative Procedure Act violation
and that the phrase should be removed
in the final rule.
Our Response: The commenters are
correct that we proposed to amend the
definition of ‘‘species.’’ In the preamble
we wrote, ‘‘Finally, we explain our
interpretation of the meaning of the
phrase ‘interbreeds when mature,’
which is found in the definition of
‘species.’ . . . Although we are not
proposing to revise the regulations at
this time, we are using this notice to
inform the public of our longstanding
interpretation of this phrase.’’ Our
intent was to explain how we have
interpreted the phrase, but by
inadvertently including this
interpretation in the regulatory language
of the proposed rule, we in fact were
proposing to change the definition of
‘‘species’’ to insert, ‘‘A distinct
population segment ‘interbreeds when
mature’ when it consists of members of
the same species or subspecies in the
wild that are capable of interbreeding
when mature.’’ We have removed the
proposed language from the definition
of ‘‘species’’ in this final rule and left
only the language in the preamble. The
Services are not amending the
definition.
(58) Comment: A commenter
suggested that the Services clarify the
meaning of ‘‘being considered by the
Secretary’’ in the definition of the term
‘‘candidate.’’ The commenter suggested
that the final rule substitute the more
narrow definition found in the FWS
candidate species fact sheet, which
states: ‘‘Candidate species are plants
and animals for which the U.S. Fish and
Wildlife Service has sufficient
information on their biological status
and threats to propose them as
endangered or threatened under the
Endangered Species Act, but for which
development of a proposed listing
regulation is precluded by other higher
priority listing activities.’’
Our Response: We agree with the
commenter that the statement in the
FWS candidate fact sheet is an
appropriate meaning of the phrase
‘‘being considered by the Secretary’’
found in the definition of candidate. We
emphasize that we did not change the
definition of ‘‘candidate’’ in this
regulation.
Criteria for Designating Critical Habitat
(59) Comment: The Western
Governors’ Association requested that
the Services provide a thorough, databased explanation of the basis for the
determination that areas outside the
range occupied at the time of listing are
or will be essential habitat.
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Our Response: Under section
3(5)(A)(ii) of the Act, to designate as
critical habitat specific areas that are
outside the geographical area occupied
by the species at the time the species is
listed, the Services must determine that
the areas are essential for the
conservation of the species. This
determination must be based on the best
scientific data available concerning the
particular species and its conservation
needs. When the Services propose to
designate specific areas pursuant to
section 3(5)(A)(ii), they have under the
existing regulations and will under the
revised regulations explain the basis for
the determination, including the
supporting data. Thus, the Services’
explanation will be available for public
comment.
(60) Comment: Several commenters,
including one State, were concerned
that the essential areas in unoccupied
areas may not even be suitable for the
species and that this is an erroneous and
unreasonable interpretation of an
otherwise clear statutory statement and
should be withdrawn.
Our Response: Section 3(5)(A)(ii) of
the Act expressly allows for the
consideration and inclusion of
unoccupied habitat in a critical habitat
designation if such habitat is
determined to be essential for the
conservation of the subject species.
These areas do not have to contain the
physical or biological features and are
not subject to a finding that they may
require special management
considerations or protection. This is in
contrast to what is required under the
first part of the definition of ‘‘critical
habitat’’ (section 3(5)(A)(i) of the Act)
for areas occupied at the time of listing.
(61) Comment: Several commenters
stated that the Services may only
properly make a ‘‘not prudent’’ finding
if there is specific information that
increased poaching would result from
designating critical habitat.
Our Response: We respectfully
disagree with the commenters’
assertion. The current regulations (49
FR 38900; October 1, 1984, and at 50
CFR 424.12(a)(1)) allow for a
determination that critical habitat is not
prudent for a species if such designation
would: (1) Increase the degree of threat
to the species through the identification
of critical habitat, or (2) not be
beneficial to the species. The
determination that critical habitat is not
prudent for a listed species is
uncommon, especially given that most
species are listed, in part, because of
impacts to their habitat or curtailment of
their range. Most ‘‘not prudent’’ findings
have resulted from a determination that
there would be increased harm or
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threats to a species through the
identification of critical habitat. For
example, if a species was highly prized
for collection or trade, then identifying
specific localities of the species could
render it more vulnerable to collection
and, therefore, further threaten it.
However, in some circumstances, a
species may be listed because of factors
other than threats to its habitat or range,
such as disease, and the species may be
a habitat generalist. In such a case, on
the basis of the existing and revised
regulations, it is permissible to
determine that critical habitat is not
beneficial and, therefore, not prudent. It
is also permissible to determine that a
designation would not be beneficial if
no areas meet the definition of ‘‘critical
habitat.’’
(62) Comment: Several commenters
inquired about whether the Services
would revise the regulations to provide
greater flexibility in defining a greater
breadth of circumstances where a
determination can be made that the
designation of critical habitat for a
species is not beneficial to its
conservation and, therefore, not
prudent.
Our Response: As noted above, it is
permissible under the current and
revised regulations to determine that
designating critical habitat for a species
is not beneficial and, therefore, not
prudent. The text of these revised
regulations further clarifies the nonexclusive list of factors the Services may
consider in evaluating whether
designating critical habitat is not
beneficial. The inclusion of ‘‘but not
limited to’’ to modify the statement ‘‘the
factors the Services may consider
include’’ allows for the consideration of
alternative fact patterns where a
determination that critical habitat is not
beneficial would be appropriate. We
think it is important to expressly reflect
this regulatory flexibility in the revised
regulations. Nonetheless, based on the
Services’ history of implementing
critical habitat, we anticipate that
making a not-prudent determination on
any fact pattern will be rare.
(63) Comment: One State commented
that the Services dropped the word
‘‘probable’’ from the revised § 424.12(a)
when talking about economic impacts
and that the word should be retained in
the final rule.
Our Response: We agree and have
retained the word ‘‘probable’’ in this
final rule. It is consistent with the
revised final regulation in 50 CFR
424.19 (78 FR 53058) and our draft
policy on exclusions under section
4(b)(2) of the Act. We note that in this
context the term ‘‘probable’’ means
reasonably likely to occur.
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(64) Comment: Several commenters
recommended adding after the word
‘‘threat’’ in the second sentence to
§ 424.12(a)(1)(ii), the words ‘‘sufficient
to warrant listing the species as
threatened or endangered.’’
Our Response: While we agree with
the commenters’ intent, we find that
adding the phrase would be redundant
because we would only be making a
determination as to whether critical
habitat is prudent if the species was
either being proposed for listing
simultaneously or is already listed.
(65) Comment: Several commenters
thought the Services should simply
delete § 424.12(a)(1)(ii) instead of
expanding it. They further stated that
the Act does not require that a species
currently be threatened by habitat loss
before critical habitat is designated and
protected, and the spirit of the Act
would not be served by the imposition
of such a requirement by regulation.
Our Response: Critical habitat is a
conservation tool under the Act that can
provide for the regulatory protection of
a species’ habitat. The current
regulations and the proposed revisions
do not establish a requirement that a
species be threatened by the
modification, fragmentation, or
curtailment of its range for critical
habitat to be beneficial and, therefore,
prudent to designate. However, the
regulation and revisions establish a
framework whereby if a species is listed
under the Act and it is determined
through that process that its habitat is
not limited or threatened by destruction,
modification, or fragmentation, then it
may not be beneficial or prudent to
designate critical habitat. While this
provision is intended to reduce the
burden of regulation in rare
circumstances in which designating
critical habitat does not contribute to
conserving the species, the Services
recognize the value of critical habitat as
a conservation tool and expect to
designate it in most cases.
(66) Comment: Several commenters
stated that § 424.12(a)(2) is not
consistent with the plain meaning of the
Act and should be deleted from the final
rule. They stated the proposed minor
word changes did not improve the
situation.
Our Response: The minor word
changes to § 424.12(a)(2) are meant to
make the language more consistent with
the language in the Act. This section is
necessary to inform the public as to the
circumstances in which the Services
will make a not-determinable finding on
critical habitat and thereby invoking the
1-year extension of section 4(b)(6)(C)(ii)
of the Act. 16 U.S.C. 1533(b)(6)(C)(ii).
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(67) Comment: A commenter stated
that when the Services deem critical
habitat as not determinable due to a lack
of data for habitat analyses or lack of
knowledge on biological needs of the
species, the Services should regularly
check for new data and/or make efforts
to collect necessary data and move
forward with critical habitat
designations. One State also commented
that critical habitat designations should
only be made based on the best
available scientific data and
information, and in instances where
data or information is lacking, the
Services have an obligation to delay a
designation until such time that
sufficient information is acquired.
Our Response: Finding that critical
habitat is not determinable only invokes
a 1-year extension of the deadline for
finalizing a critical habitat designation
under section 4(b)(6)(C)(ii) of the Act. 16
U.S.C. 1533(b)(6)(C)(ii). At the
conclusion of the year, the Services
must move forward with the designation
and have no authority under the Act to
further delay designation (unless we
determine that designation is not
prudent). We agree that critical habitat
designations must only be made based
on the best scientific data available as
required by the Act. If we initially do
not have enough data to make a critical
habitat determination, then we can
invoke the 1-year extension allowed
under the Act. The Services use that
time to gather additional data. At the
end of the 1-year extension, the Services
must use the best scientific data
available to make the critical habitat
determination.
(68) Comment: One State suggested
that climate change is more
appropriately addressed during a 5-year
status review and the critical habitat
revision process than trying to attempt
to accommodate future critical habitat
by predicting areas necessary to support
the species’ recovery. It further asserted
that the Services’ proposed authority to
designate areas that are currently
unoccupied and which are not now
necessary to support the species’
recovery, but may eventually become
necessary, is a vast expansion of the
critical habitat program and contrary to
the focus in the Act on current habitat
conditions.
Our Response: We agree that 5-year
status reviews and the critical habitat
revision process can play important
roles regarding the conservation needs
of a species in response to habitat
changes resulting from climate change.
However, the statute as written allows
for sufficient flexibility to address the
effects of climate change in a critical
habitat designation, and, therefore, the
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clarifications provided in our proposal
and this final rule do not expand the
Services’ authority. There have been
specific circumstances, as discussed in
our proposal, where data have been
available showing the shift in habitat
use by a species in response to the
effects of climate change. In those cases
where the best scientific data available
indicate that a species may be shifting
habitats or habitat use, then it is
permissible to include specific areas
accommodating these changes in a
designation, provided that the Services
can explain why the areas meet the
definition of ‘‘critical habitat.’’ Although
some such instances are based on
reasonable predictions of how habitat
will be used by the species in the future,
they are based on determinations that
the areas are currently essential to the
species. In other words, we may find
that an unoccupied area is currently
‘‘essential for the conservation’’ even
though the functions the habitat is
expected to provide may not be used by
the species until a point in the
foreseeable future. The data and
rationale on which such a designation is
based will be clearly articulated in our
proposed rule designating critical
habitat. The Services will consider
whether habitat is occupied or
unoccupied when determining whether
to designate it as critical habitat and use
the best available scientific data on a
case-by-case basis regarding the current
and future suitability of such habitat for
recovery of the species, and when
developing conservation measures.
(69) Comment: Several commenters
requested clarification of new
§ 424.12(e) with regard to the
differences in the way the Services
handle designation of critical habitat for
species listed prior to the 1982
amendments to the Act versus species
listed after the 1982 amendments.
Our Response: If the Services
designate critical habitat for species
listed prior to the 1982 amendments, the
designation is procedurally treated like
a revision of existing critical habitat
even if critical habitat was never
designated. Thus, the Services have
additional options at the final rule stage
with regard to a proposal to designate
critical habitat for those species listed
prior to 1982 that they do not have
when proposing to designate habitat for
other species. These include an option
to make a finding that the revision
‘‘should not be made’’ and to extend the
12-month deadline by an additional
period of up to 6 months if there is
substantial disagreement regarding the
sufficiency or accuracy of available data
(see 16 U.S.C. 1533(b)(6)(B)(i)).
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(70) Comment: Several commenters,
including two States, indicated that
removing references to ‘‘primary
constituent elements’’ dramatically and
unnecessarily expands the scope of
critical habitat and confuses instead of
clarifies critical habitat designation,
leading to more litigation.
Our Response: Removing references to
‘‘primary constituent elements’’ from
the regulation will not result in
expansion of the scope of critical
habitat. Removing this phrase is not
intended to substantively alter anything
about the designation of critical habitat,
but to eliminate redundancy in how we
describe the physical or biological
features. The phrase ‘‘primary
constituent element’’ is not found in the
Act and the regulations have never been
clear as to how primary constituent
elements relate to or are distinct from
physical or biological features essential
to the conservation of the species,
which is the phrase used in the Act. In
fact, the removal of the phrase ‘‘primary
constituent elements’’ will alleviate the
tension caused by trying to understand
the relationship between the phrases.
The specificity of the primary
constituent elements that has been
discussed in previous designations will
now be discussed in the descriptions of
the physical or biological features
essential to the conservation of the
species.
(71) Comment: Several commenters
including several States were opposed
to elimination of § 424.12(e) as this
section is necessary and intentionally
limiting and is an accurate
implementation of the statutory
definition and Congressional intent.
Several commenters also questioned
that when the Services promulgated
§ 424.12(e) in 1980, that we explained in
the preamble to that rule that the
limitation in § 424.12(e) was intended to
‘‘implement the statutory requirement’’
that unoccupied areas may be
designated ‘‘only if necessary to ensure
the conservation of the species.’’ The
Services do not address this prior
interpretation at all, or explain why a
rule that it once enacted as necessary to
implement a statutory requirement is
now unnecessary.
Our Response: We respectfully
disagree. Section 424.12(e) did not
allow us to designate unoccupied areas
unless a designation limited to its
present range (occupied) would be
inadequate to ensure the conservation of
the species. As we stated in the
proposed rule, there is no suggestion in
the legislative history that the Services
were expected to exhaust occupied
habitat before considering whether any
unoccupied areas may be essential.
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Further, section 3(5)(A) of the Act
expressly allows for the consideration
and inclusion of unoccupied habitat in
a critical habitat designation if such
habitat is determined to be essential for
the conservation of the subject species.
There is no specific language in the Act
that requires the Services to first prove
that the inclusion of all occupied areas
in a designation are insufficient to
conserve the species before considering
unoccupied areas. However, the existing
implementing regulations state that
such unoccupied habitat could only be
considered if a determination was made
that the Service(s) could not recover the
species with the inclusion of only the
occupied habitat.
We have learned from years of
implementing the critical habitat
provisions of the Act that often a rigid
step-wise approach, i.e., first
designating all occupied areas that meet
the definition of ‘‘critical habitat’’
(assuming that no unoccupied habitat is
designated) and then, only if that is not
enough, designating essential
unoccupied habitat, does not
necessarily serve the best conservation
strategy for the species and in some
circumstances may result in a
designation that is geographically larger,
but less effective as a conservation tool.
Our proposed change will allow us to
consider the inclusion of occupied and
unoccupied areas in a critical habitat
designation following at minimum a
general conservation strategy for the
species. In some cases, we have and
may continue to find, that the inclusion
of all occupied habitat in a designation
does not support the best conservation
strategy for a species. We expect that the
concurrent evaluation of occupied and
unoccupied areas for a critical habitat
designation will allow us to develop
more precise and deliberate
designations that can serve as more
effective conservation tools.
Additionally, there is no specific
language in the Act that requires the
Services to first prove that the inclusion
of all occupied areas in a designation
are insufficient to conserve the species
before considering unoccupied areas.
The statutory language is sufficiently
clear that it does not need explanation
in the revised regulation, and, moreover,
to the extent that the 1980 regulation
language differs from the statutory
language, it does not add any clarity.
(72) Comment: Several commenters,
including one State, disagreed that
unoccupied areas need not have the
features essential to the conservation of
the species and that the Services
propose to unlawfully write this
statutory requirement out of the Act.
The State also pointed out that the
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Services’ current position on this issue
is distinctly contrary to the position the
Services took in 1984 when the existing
regulations were adopted.
Our Response: Under the second part
of the definition of ‘‘critical habitat’’ in
the Act (section 3(5)(A)(ii)), the Services
are to identify specific areas outside the
geographical area occupied by the
species, at the time it is listed in
accordance with the provisions of
section 4 of the Act, upon a
determination by the Secretary that such
areas are essential for the conservation
of the species. In contrast to section
3(5)(A)(i), this provision does not
mention physical or biological features,
much less require that the specific areas
contain the physical or biological
features essential to the conservation of
the species. These are two clearly
distinct provisions. The unoccupied
areas do not have to presently contain
any of the physical or biological
features, which is not a change from the
way we have been designating
unoccupied critical habitat (see, e.g.,
Markle Interests v. USFWS, 40 F. Supp.
3d 744 (E.D. La. 2014)).
(73) Comment: One State
recommended that the Services develop
a policy or metric to determine whether
a particular area should be designated as
critical habitat in unoccupied areas.
Our Response: This final rule explains
the Services’ general parameters for
designating critical habitat. The details
of why a specific area is determined to
be essential to the conservation of the
species will in part be directed by any
generalized conservation strategy
developed for the species, and clearly
articulated in our proposed and final
rules designating critical habitat. That
determination is a fact-specific analysis
and is based on the best available
scientific data for the species and its
conservation needs. The proposed rule
for each critical habitat designation will
be subject to public review and
comment.
(74) Comment: A commenter
suggested that the Services designate
enough critical habitat at the time of
listing to ensure that a species can
recover.
Our Response: In evaluating which
areas qualify as critical habitat and
specific areas finalized (subject to
section 4(b)(2) exclusions, see final
policy published elsewhere in today’s
Federal Register), we follow the
statutory requirements to identify those
occupied areas that contain the physical
or biological features essential to the
species’ conservation that may require
special management considerations or
protection and any unoccupied areas
that we determine to be essential for the
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species’ conservation. Designation of
critical habitat is one important tool that
contributes to recovery, but a critical
habitat designation alone may not be
sufficient to achieve recovery. Indeed,
given the limited regulatory role of a
critical habitat designation (i.e., through
section 7’s mandate that Federal
agencies avoid destruction or adverse
modification of critical habitat, see final
rule published elsewhere in today’s
Federal Register), it is generally not
possible to look to a critical habitat
designation alone to ensure recovery.
Also, we must designate critical habitat
according to mandatory timeframes,
very often prior to development of a
formal recovery plan. See Home
Builders Ass’n of Northern Cal. v. U.S.
Fish and Wildlife Service, 616 F.3d 983,
989–90 (9th Cir. 2010). However,
although a critical habitat designation
will not necessarily ensure recovery, it
will further recovery because the
Services base the designation on the
best available scientific information
about the species’ habitat needs at the
time of designation. The best available
information will include any
generalized conservation strategy or
criteria that may have been developed
for the species in consultation with staff
working in recovery planning and
implementation to ensure collaboration,
consistency, and efficiency as the
Services work with the public and
partners to recover a listed species.
(75) Comment: A commenter stated
that the proposed rule clarifies that the
Services have the discretion to designate
critical habitat for species listed before
1978, but does not specify when that
discretion would be used. The
commenter requested that the Services
identify guidelines or standards for
judging when to designate critical
habitat for pre-1978 species.
Our Response: Whether to exercise
discretion to designate critical habitat
for species listed prior to 1978 is a casespecific determination dependent on the
conservation needs of the species,
scientific data available, and the
resources available for additional
rulemaking. Guidelines on this point
could limit Secretarial discretion and
may not allow for sufficient flexibility
in furthering the conservation of a
species.
(76) Comment: Several commenters
were concerned that the Services must
commit to using the best scientific data
available when designating unoccupied
areas as critical habitat.
Our Response: We are mandated by
the Act to use (and are committed to
using) the best scientific data available
in determining any specific areas as
critical habitat, regardless of occupancy.
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(77) Comment: Several Tribes stated
that while the Services readily
acknowledge in the proposal their
responsibility to communicate
meaningfully with recognized Federal
Tribes on a government-to-government
basis, the proposed revision does
nothing to clarify how the Services will
carry out this responsibility.
Our Response: These revised
regulations set forth our general practice
for designating critical habitat, clarify
definitions and phrases, and in general
align the regulations with the statute.
The revised regulations are not intended
to be prescriptive in how the Services
will implement the provisions or
coordinate with federally recognized
Tribes that are potentially affected.
However, the Services are committed to
communicate and coordinate
meaningfully and effectively with
federally recognized Tribes concerning
actions under the ESA, including the
development and implementation of
critical habitat for species that may
occur on their lands. We rely on the
requirements of S.O. 3206 to provide the
guidance on how the Services will carry
out this responsibility. We have often
found that the best and most meaningful
coordination and collaboration,
including fulfilling our responsibilities
under S.O. 3206, occurs between our
Regional and field offices and a specific
Tribe on a particular species.
(78) Comment: Several commenters
were opposed to the inclusion of the
proposed § 424.12(g), saying the Act
makes no distinction between foreign
and domestic species and requires that
all listed species receive critical habitat
unless doing so is not prudent or
determinable.
Our Response: We respectfully
disagree. Subsection (g) is a
continuation of existing subsection (h),
which has long codified the Services’
understanding that critical habitat
should not be designated outside of
areas under United States jurisdiction.
This interpretation is well supported.
The Act makes a distinction between
coordination with and implementation
of the provisions of the ESA between
States and local jurisdictions within the
United States versus with foreign
countries. Section 4(b)(1)(A), which
deals with listing species, provides that
the Secretary shall consult, as
appropriate, not only with affected
States, but also, in cooperation with the
Secretary of State, with the country or
countries in which the species is
normally found. In contrast, section 7 of
the ESA does not include a requirement
to consult with foreign governments.
Further, section 8(b)(1) states that ‘‘the
Secretary, through the Secretary of
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State, shall encourage—(1) foreign
countries to provide for the
conservation of fish or wildlife and
plants including endangered species
and threatened species listed pursuant
to section 4.’’ It is clear that Congress
understood the distinction between
implementing the ESA within the
jurisdiction of the United States and
implementing the ESA within the
jurisdiction of foreign countries. It then
follows that since Congress did not
explicitly state that critical habitat shall
be designated in foreign countries or
that the Secretary consult, as
appropriate, with foreign countries on a
designation of critical habitat, then the
designation of critical habitat is limited
to lands within the jurisdiction of the
United States.
Justice Stevens approved of the
Services’ conclusion in his concurrence
in Lujan v. Defenders of Wildlife, 504
U.S. 555 (1992). There, he favorably
noted the Service’s longstanding
interpretation of the limitation of
critical habitat designations to areas
within the jurisdiction of the United
States:
The Secretary of the Interior and the
Secretary of Commerce have consistently
taken the position that they need not
designate critical habitat in foreign countries.
See 42 FR 4869 (1977) (initial regulations of
the Fish and Wildlife Service and the
National Marine Fisheries Service on behalf
of the Secretary of the Interior and the
Secretary of Commerce). Consequently,
neither Secretary interprets § 7(a)(2) to
require federal agencies to engage in
consultations to ensure that their actions in
foreign countries will not adversely affect the
critical habitat of endangered or threatened
species.
That interpretation is sound. . . .
Id. at 587 (Stevens, J., concurring).
(79) Comment: One State requested
that the Services include a new
§ 424.12(e) that requires that designation
will be made after consultation with the
affected States. It would read, ‘‘In
designating any area as critical habitat,
the Secretary shall consult with affected
States (those in which the proposed
critical habitat is located or those that
may be affected by the designation of
the habitat) prior to completing the
designation, and the fact of and finding
of such consultation shall be addressed
in the final rulemaking for the
designation.’’
Our Response: The suggested new
§ 424.12(e) is not necessary because
section 4(b)(5)(A)(ii) of the Act requires
the Secretary to give actual notice of the
proposed regulation (including the
complete text of the regulation) to the
State agency in each State in which the
species is believed to occur, and to each
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county or equivalent jurisdiction in
which the species is believed to occur,
and invite the comment of such agency,
and each such jurisdiction. Further,
section 4(i) of the Act requires the
Secretary to provide a written
justification for adopting regulations in
conflict with the agency’s comments or
for failing to adopt a regulation as
requested in a State petition. In addition
to these requirements, the Services are
committed to continuing to work with
the States early in the process to ensure
that we are using the best scientific data
available.
(80) Comment: One State requested
clarification on the application of this
regulation to critical habitat
designations that are currently under
way, but not yet finalized.
Our Response: As indicated in DATES
above, although effective 30 days from
the date of publication, the revised
version of § 424.12 will apply only to
rulemakings for which the proposed
rule is published after that date. Thus,
the prior version of § 424.12 will
continue to apply to any rulemakings
for which a proposed rule was
published before that date. However,
because many of the revisions merely
codify or explain our existing practices
and interpretations, we may
immediately refer to and act consistent
with the amended language of § 424.12
in final rules to which the prior version
applies.
(81) Comment: Several commenters
objected to the Services’ determination
that a regulatory flexibility analysis is
not required for this regulation, stating
the regulated community is affected by
this regulation.
Our Response: We respectfully
disagree. We interpret the Regulatory
Flexibility Act, as amended, to require
that Federal agencies evaluate the
potential incremental impacts of
rulemaking only on those entities
directly regulated by the rulemaking
itself and, therefore, not on indirectly
regulated entities. Recent case law
supports this interpretation (https://
www.sba.gov/sites/default/files/
rfaguide_0512_0.pdf, pages 22–23).
NMFS and FWS are the only entities
that are directly affected by this rule
because we are the only entities that
designate critical habitat, and this rule
pertains to the procedures for carrying
out those designations. No external
entities, including any small businesses,
small organizations, or small
governments, will experience any direct
economic impacts from this rule.
We understand that there is
considerable confusion as to how these
revisions to the regulation will change
the process for designating critical
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habitat, with many thinking it will
greatly expand our designations and
provide less clarity to the process. We
went to great effort in our proposal and
further in this final rule to explain that
revised regulations will not result in any
significant deviation from how the two
agencies have been designating critical
habitat. Our intent is to codify what we
have been doing for many years and
provide common-sense revisions based
on lessons learned and relevant case
law. It is our expectation that these
revisions will allow us to develop more
precise and deliberate designations that
can serve as more effective conservation
tools, focusing conservation resources
where needed and minimizing
regulatory burdens where not necessary.
As a consequence, we find, as iterated
above, that NMFS and FWS are the only
entities directly regulated by these
revisions and that an RFA analysis is
not required.
(82) Comment: We received several
comments that the proposed revised
regulations constituted a major Federal
action because they will result in
significant socioeconomic consequences
and these impacts must be analyzed
under the National Environmental
Policy Act of 1969 (NEPA).
Our Response: As detailed in the
REQUIRED DETERMINATIONS section
below, we have determined that this
action qualifies for a categorical
exclusion under both DOI and NOAA
governing procedures.
Final Amendments to Regulations
Discussion of Changes to Part 424
This final rule revises 50 CFR 424.01,
424.02, and 424.12 (except for
paragraph (c)) to clarify the procedures
and criteria used for designating critical
habitat, addressing in particular several
key issues that have been subject to
frequent litigation.
In finalizing the specific changes to
the regulations that follow, and setting
out the accompanying clarifying
discussion in this preamble, the
Services are establishing prospective
standards only. As indicated in DATES
above, although effective 30 days from
the date of publication, the revised
version of § 424.12 will apply only to
rulemakings for which the proposed
rule is published after that date. Thus,
the prior version of § 424.12 will
continue to apply to any rulemakings
for which a proposed rule was
published before that date. However,
because many of the revisions merely
codify or explain our existing practices
and interpretations, we may
immediately refer to and act consistent
with the amended language of § 424.12
in final rules to which the prior version
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applies. Nothing in these final revised
regulations is intended to require that
any previously completed critical
habitat designation must be reevaluated
on this basis.
Section 424.01 Scope and Purpose
We are making minor revisions to this
section to update language and
terminology. The first sentence in
§ 424.01(a) is being revised to remove
reference to critical habitat being
designated or revised only ‘‘where
appropriate.’’ This wording implied a
greater flexibility regarding whether to
designate critical habitat than is correct.
Circumstances in which we determine
critical habitat designation is not
prudent are rare. Therefore, the new
language removes the phrase ‘‘where
appropriate.’’ Other revisions to this
section are minor word changes to use
more plain language or track the
statutory language.
Section 424.02 Definitions
This section of the regulations defines
terms used in the context of section 4 of
the Act. We are making revisions to
§ 424.02 to update it to current
formatting guidelines, to revise several
definitions related to critical habitat, to
delete definitions that are redundant
with statutory definitions, and to add
two newly defined terms. Section
424.02 is currently organized with
letters as paragraph designation for each
term (e.g., § 424.02(b) Candidate). The
Office of the Federal Register now
recommends setting out definitions in
the CFR without paragraph
designations. We propose to revise the
formatting of the entire section
accordingly. Discussion of the revised
definitions and newly defined terms
follows. We note where these final
revisions differ from those set out in the
proposed rule.
We note that, although revising the
formatting of the section requires that
the entirety of the section be restated in
the final-amended-regulation section,
we are not at this time revisiting the text
of those existing definitions that we are
not specifically revising, including
those that do not directly relate to
designating critical habitat. In
particular, we are not in this rulemaking
amending the definitions of ‘‘plant,’’
‘‘wildlife,’’ or ‘‘fish and wildlife’’ to
reflect changes in taxonomy since the
ESA was enacted in 1973. In 1973, only
the Animal and Plant Kingdoms of life
were universally recognized by science,
and all living things were considered to
be members of one of these kingdoms.
Thus, at enactment, the ESA applied to
all living things. Advances in taxonomy
have subsequently split additional
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kingdoms from these two. Any species
that was considered to be a member of
the Animal or Plant Kingdoms in 1973
will continue to be treated as such for
purposes of the administration of the
Act regardless of any subsequent
changes in taxonomy. We may address
this issue in a future rulemaking relating
to making listing determinations (as
opposed to designating critical habitat).
In the meantime, the republication of
these definitions here should not be
viewed as an agency determination that
these definitions reflect the scope of the
Act in light of our current
understanding of taxonomy.
The current regulations include a
definition for ‘‘Conservation, conserve,
and conserving.’’ We are revising the
title of this entry to ‘‘Conserve,
conserving, and conservation,’’
changing the order of the words to
conform to the statute. Additionally, we
are revising the first sentence of the
definition to include the phrase ‘‘i.e.,
the species is recovered’’ to clarify the
link between conservation and recovery
of the species. The statutory definition
of ‘‘conserve, conserving, and
conservation’’ is ‘‘to use and the use of
all methods and procedures that are
necessary to bring any endangered or
threatened species to the point at which
measures provided pursuant to the Act
are no longer necessary.’’ This is the
same concept as the definition of
‘‘recovery’’ found in § 402.02:
‘‘improvement in the status of listed
species to the point at which listing is
no longer appropriate.’’ The Services,
therefore, view ‘‘conserve, conserving,
and conservation’’ as a process
culminating at the point at which a
species is recovered.
We are deleting definitions for
‘‘critical habitat,’’ ‘‘endangered species,’’
‘‘plant,’’ ‘‘Secretary,’’ ‘‘State Agency,’’
and ‘‘threatened species’’ because these
terms are defined in the Act and the
existing regulatory definitions do not
add meaning to the terms.
We also define the previously
undefined term ‘‘geographical area
occupied by the species’’ as: ‘‘the
geographical area which may generally
be delineated around the species’
occurrences, as determined by the
Secretary (i.e., range). Such areas may
include those areas used throughout all
or part of the species’ life cycle, even if
not used on a regular basis (e.g.,
migratory corridors, seasonal habitats,
and habitats used periodically, but not
solely by vagrant individuals).’’ This
term appears in the definition of
‘‘critical habitat’’ found in section
3(5)(A)(i) and (ii) of the Act, but is not
defined in the Act or in our current
regulations. The inclusion of this new
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regulatory definition reflects the
Services’ efforts to clarify the criticalhabitat-designation process.
The definition of ‘‘critical habitat’’ in
the Act has two parts, section 3(5)(A)(i)
and (ii), which establish two distinct
categories of critical habitat, based on
species occupancy in an area at the time
of listing. Therefore, to identify specific
areas to designate as critical habitat, we
must first determine what area
constitutes the ‘‘geographical area
occupied by the species at the time of
listing,’’ which is the language used in
the Act. The scale of this area is likely
to be larger than the specific areas that
would then be analyzed for potential
designation under section 3(5)(A)(i).
This is because the first part of the
critical habitat definition in the Act
directs the Services to identify ‘‘specific
areas within’’ the geographical area
occupied by the species at time of
listing. This intentional choice to use
more narrow terminology alongside
broader terminology suggests that the
‘‘geographical area’’ was expected most
often to be a larger area that could
encompass multiple ‘‘specific areas.’’
Thus, we find the statutory language
supports the interpretation of equating
the geographical area occupied by the
species to the wider area around the
species’ occurrences at the time of
listing. A species’ occurrence is a
particular location in which members of
the species are found throughout all or
part of their life cycle. The geographic
area occupied by the species is thus the
broader, coarser-scale area that
encompasses the occurrences, and is
what is often referred to as the ‘‘range’’
of the species.
In the Act, the term ‘‘geographical
area occupied by the species’’ is further
modified by the clause ‘‘at the time it is
listed.’’ However, if critical habitat is
being designated or revised several
years after the species was listed, it can
be difficult to discern what was
occupied at the time of listing. The
known distribution of a species can
change after listing for many reasons,
such as discovery of additional
localities, extirpation of populations, or
emigration of individuals to new areas.
In many cases, information concerning
a species’ distribution, particularly on
private lands, is limited as surveys are
not routinely carried out on private
lands unless performed as part of an
environmental analysis for a particular
development proposal. Even then, such
surveys typically focus on listed rather
than unlisted species, so our knowledge
of a species’ distribution at the time of
listing in these areas is often limited and
the information in our listing rule may
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not detail all areas occupied by the
species at that time.
Thus, while some of these changes in
a species’ known distribution reflect
changes in the actual distribution of the
species, some reflect only changes in the
quality of our information concerning
distribution. In these circumstances, the
determination of which geographic
areas were occupied at the time of
listing may include data developed
since the species was listed. This
interpretation was supported by a recent
court decision, Otay Mesa Property L.P.
v. DOI, 714 F. Supp. 2d 73 (D.D.C.
2010), rev’d on other grounds, 646 F.3d
914 (D.C. Cir. 2011) (San Diego fairy
shrimp). In that decision, the judge
noted that the clause ‘‘occupied at the
time of listing’’ allows FWS to make a
post-listing determination of occupancy
based on the currently known
distribution of the species in some
circumstances. Although the D.C.
Circuit disagreed with the district court
that the record contained sufficient data
to support the FWS’ determination of
occupancy in that case, the D.C. Circuit
did not express disagreement with (or
otherwise address) the district court’s
underlying conclusion that the Act
allows FWS to make a post-listing
determination of occupancy if based on
adequate data. The FWS acknowledges
that to make a post-listing determination
of occupancy we must distinguish
between actual changes to species
occupancy and changes in available
information. For succinctness, herein
and elsewhere we refer to areas as
‘‘occupied’’ when we mean ‘‘occupied
at the time of listing.’’
The second sentence of the definition
for ‘‘geographical area occupied by the
species’’ clarifies that the meaning of
the term ‘‘occupied’’ includes specific
areas that are used only periodically or
temporarily by a listed species during
some portion of its life history, and is
not limited to those areas where the
listed species may be found more or less
continuously. Areas of periodic use may
include, for example, breeding areas,
foraging areas, and migratory corridors.
The Ninth Circuit recently supported
this interpretation by FWS, holding that
a determination that a species was likely
to be temporarily present in the areas
designated as critical habitat was a
sufficient basis for determining those
areas to be occupied, even if the species
was not continuously present. Arizona
Cattle Growers’ Assoc. v. Salazar, 606
F.3d 1160 (9th Cir. 2010) (Mexican
spotted owl).
Nonetheless, periodic use of an area
does not include use of habitat in that
area by vagrant individuals of the
species who wander far from the known
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range of the species. Occupancy by the
listed species must be based on
evidence of regular periodic use by the
listed species during some portion of
the listed species’ life history. However,
because some species are difficult to
survey or we may otherwise have
incomplete survey information, the
Services will rely on the best available
scientific data, which may in some cases
include indirect or circumstantial
evidence, to determine occupancy. We
further note that occupancy does not
depend on identifiable presence of adult
organisms. For example, periodical
cicadas occupy their range even though
adults are only present for 1 month
every 13 or 17 years. Similarly, the
presence (or reasonably determined
presence) of eggs or cysts of fairy shrimp
or seed banks of plants constitute
occupancy even when mature
individuals are not present.
We also finalize a definition for the
term ‘‘physical or biological features.’’
This phrase is used in the statutory
definition of ‘‘critical habitat’’ to assist
in identifying the specific areas within
the entire geographical area occupied by
the species that can be considered for
designation as critical habitat. We
define ‘‘physical or biological features’’
as ‘‘the features that support the lifehistory needs of the species, including
but not limited to water characteristics,
soil type, geological features, sites, prey,
vegetation, symbiotic species, or other
features. A feature may be a single
habitat characteristic, or a more
complex combination of habitat
characteristics. Features may include
habitat characteristics that support
ephemeral or dynamic habitat
conditions. Features may also be
expressed in terms relating to principles
of conservation biology, such as patch
size, distribution distances, and
connectivity.’’
The definition clarifies that physical
and biological features can be the
features that support the occurrence of
ephemeral or dynamic habitat
conditions. For example, a species may
require early-successional riparian
vegetation in the Southwest to breed or
feed. Such vegetation may exist only 5
to 15 years after a local flooding event.
The necessary features, then, may
include not only the suitable vegetation
itself, but also the flooding events,
topography, soil type, and flow regime,
or a combination of these characteristics
and the necessary amount of the
characteristics that can result in the
periodic occurrence of the suitable
vegetation. Thus, the Services could
conclude that essential physical or
biological features exist in a specific
area even in the temporary absence of
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suitable vegetation, and could designate
such an area as critical habitat if all of
the other applicable requirements were
met and if there were documented
occurrences of the particular habitat
type in the area and a reasonable
expectation of that habitat occurring
again.
In Cape Hatteras Access Preservation
Alliance v. DOI, 344 F. Supp. 2d 108,
123 n.4 (D.D.C. 2004), the court rejected
FWS’ designation for the piping plover
as including lands that did not currently
contain the features defined by FWS,
but noted that it was not addressing
‘‘whether dynamic land capable of
supporting plover habitat can itself be
one of the ‘physical or biological
features’ essential to conservation.’’ The
new definition for ‘‘physical or
biological features’’ clarifies that
features can be dynamic or ephemeral
habitat characteristics. However, an area
within the geographical area occupied
by the species, containing habitat that is
not ephemeral by nature but that has
been degraded in some way, must have
one or more of the physical or biological
features at the time of designation.
Having defined ‘‘physical or
biological features,’’ we are also
removing the term ‘‘primary constituent
element’’ and all references to it from
the regulations in § 424.12. As with all
other aspects of these revisions, this will
apply only to future critical habitat
designations and is further explained
below in the discussion of the changes
to § 424.12, where the term is currently
used.
We are also revising the definition of
‘‘special management considerations or
protection’’ which is found in § 424.02.
Here we remove the phrase ‘‘of the
environment’’ from the current
regulation. This phrase is not used in
this context elsewhere in the regulations
or the Act and, therefore, may create
ambiguity. We also insert the words
‘‘essential to’’ to conform to the
language of the Act.
In determining whether an area has
essential features that may require
special management considerations or
protection, the Services do not base
their decision on whether management
is currently in place or whether that
management is adequate. FWS formerly
took the position that special
management considerations or
protection was required only if
whatever management was in place was
inadequate and that additional special
management was needed. This position
was rejected by the court in Center for
Biological Diversity v. Norton, 240 F.
Supp. 2d 1090 (D. Ariz. 2003) (Mexican
spotted owl), the only court to address
this issue. The Services agree with the
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conclusion of the court on this point—
it is incorrect to read the statute as
asking whether additional special
management considerations or
protection may be required. The
evaluation of whether features in an
area may require special management
considerations or protection occurs
independent of whether any form of
management or protection occurs in the
area.
We expect that, in most
circumstances, the physical or
biological features essential to the
conservation of endangered species may
require special management in all areas
in which they occur, particularly for
species that have significant habitatbased threats. However, if in some areas
the essential features do not require
special management consideration or
protection because there are no
applicable threats to the features that
have to be managed or protected for the
conservation of the species, then that
area does not meet this part (section
3(5)(A)(i)) of the definition of ‘‘critical
habitat.’’ Nevertheless, we expect such
circumstances to be rare.
Furthermore, it is not necessary that
a feature currently requires special
management considerations or
protection, only that it may require
special management to meet the
definition of ‘‘critical habitat.’’ 16 U.S.C.
1532(5)(A)(i) (emphasis added). Two
district court decisions have
emphasized this point. CBD v. Norton
(Mexican spotted owl); Cape Hatteras
Access Preservation Alliance v. DOI,
344 F. Supp. 2d 108 (D.D.C. 2004)
(piping plover). The legislative history
supports the view that Congress
purposely set the standard as ‘‘may
require.’’ Earlier versions of the bills
that led to the statutory definition of
‘‘critical habitat’’ used the word
‘‘requires,’’ but ‘‘may require’’ was
substituted prior to final passage. In any
case, an interpretation of a statute
should give meaning to each word
Congress chose to use, and our
interpretation gives the word ‘‘may’’
meaning.
Finally, we explain our interpretation
of the meaning of the phrase
‘interbreeds when mature,’ which is
found in the definition of ‘species.’ The
‘‘interbreeds when mature’’ language is
ambiguous (Modesto Irrigation Dist. v.
Gutierrez, 619 F.3d 1024, 1032 (9th Cir.
2010)). Although we are not revising the
regulatory definition of ‘‘species’’ at this
time, we are using this notice to inform
the public of our interpretation of this
phrase.’’ We have always understood
the phrase ‘‘interbreeds when mature’’
to mean that a DPS consists of members
of the same species or subspecies that
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when in the wild would be biologically
capable of interbreeding if given the
opportunity, but all members need not
actually interbreed with each other. A
DPS is a subset of a species or
subspecies, and cannot consist of
members of different species or
subspecies. The ‘‘biological species’’
concept, which defines species
according to a group of organisms’
actual or potential ability to interbreed,
and their relative reproductive isolation
from other organisms, is one widely
accepted approach to defining species.
We interpret the phrase ‘‘interbreeds
when mature’’ to reflect this
understanding and to signify only that
a DPS must be composed solely of
members of the same species or
subspecies. As long as this requirement
is met, a DPS may include multiple
groups of vertebrate organisms that do
not actually interbreed with each other.
For example, a DPS may consist of
multiple groups of a fish species
separated into different drainages.
While it is possible that the members of
these groups do not actually interbreed
with each other, their members are
biologically capable of interbreeding.
Our intent was to explain how we
have interpreted the phrase, but by
inadvertently including this
interpretation in the regulatory language
of the proposed rule, we in fact were
proposing to change the definition of
‘‘species’’ to insert, ‘‘A distinct
population segment ‘interbreeds when
mature’ when it consists of members of
the same species or subspecies in the
wild that are capable of interbreeding
when mature.’’ We have removed the
proposed language from the definition
of ‘‘species’’ in this final rule and left
only the language in this preamble. We
also noticed that we inadvertently left
out the word ‘‘Includes’’ from the
definition of ‘‘species’’ in our proposed
regulation. We have restored the word
‘‘Includes’’ in this final regulation to
match the definition of ‘‘species’’ found
in our 1984 regulation. The Services are
not substantively amending the
definition at this time.
Section 424.12 Criteria for Designating
Critical Habitat
We are revising the first sentence of
paragraph (a) to clarify that critical
habitat shall be proposed and finalized
‘‘to the maximum extent prudent and
determinable . . . concurrent with
issuing proposed and final listing rules,
respectively.’’ The language of the
existing regulation is ‘‘shall be specified
to the maximum extent prudent and
determinable at the time a species is
proposed for listing.’’ We added the
words ‘‘proposed and finalized’’ to be
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consistent with the Act, which requires
that critical habitat be finalized
concurrent with listing to the maximum
extent prudent and determinable. The
existing language could be interpreted
to mean proposing critical habitat
concurrent with listing was the only
requirement. Additionally, the existing
phrase ‘‘shall be specified’’ is vague and
not consistent with the requirement of
the Act, which is to propose and finalize
a designation of critical habitat. The last
two sentences in paragraph (a) contain
minor language changes to use the
active voice.
Paragraphs (a)(1) and (a)(1)(i) are not
changed.
The first sentence of paragraph
(a)(1)(ii) remains the same. However, we
add a second sentence to paragraph
(a)(1)(ii) to provide examples of factors
that we may consider in determining
whether a designation would not be
beneficial to the species. A designation
may not be beneficial and, therefore, not
prudent, under certain circumstances,
including but not limited to: Whether
the present or threatened destruction,
modification, or curtailment of a
species’ habitat or range is not a threat
to the species, or whether no areas meet
the definition of ‘‘critical habitat.’’ For
example, this provision may apply to a
species that is threatened primarily by
disease but the habitat that it relies
upon continues to exist unaltered
throughout an appropriate distribution
that, absent the impact of the disease,
would support conservation of the
species. Another example is a species
that occurs in portions of the United
States and a foreign nation. In the
foreign nation, there are multiple areas
that have the features essential to the
conservation of the species; however, in
the United States there are no such
areas. Consequently, there are no areas
within the United States that meet the
definition of ‘‘critical habitat’’ for the
species. Therefore, there is no benefit to
designation of critical habitat, and
designation is not prudent.
While this provision is intended to
reduce the burden of regulation in rare
circumstances in which designation of
critical habitat does not contribute to
the conservation of the species, the
Services recognize the value of critical
habitat as a conservation tool and expect
to designate it in most cases.
Section 424.12(a)(2) remains
unchanged from the current regulation,
and subparagraphs (i) and (ii) contain
minor language changes to be consistent
with the language in the Act.
The Services are completely revising
§ 424.12(b) of the current regulations.
For the reason explained below, we also
remove the terms ‘‘principal biological
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or physical constituent elements’’ and
‘‘primary constituent elements’’ from
this section. These concepts are
replaced by the statutory term ‘‘physical
or biological features,’’ which we define
as described above.
The first part of the statutory
definition of ‘‘critical habitat’’ (section
3(5)(A)(i)) contains terms necessary for
(1) identifying specific areas within the
geographical area occupied by the
species that may be considered for
designation as critical habitat and (2)
describing which features on those areas
are essential to the conservation of
species. In addition, current § 424.12(b)
introduced the phrase ‘‘primary
constituent elements.’’ However, the
regulations are not clear as to how
primary constituent elements relate to
or are distinct from physical or
biological features, which is the term
used in the statute. Adding a term not
found in the statute that is at least in
part redundant with the term ‘‘physical
or biological features’’ has proven
confusing. Trying to parse features into
elements and give them meaning
distinct from one another has added an
unnecessary layer of complication and
confusion during the designation
process.
The definition of ‘‘physical or
biological features,’’ described above,
encompasses similar habitat
characteristics as currently described in
§ 424.12(b), such as roost sites, nesting
grounds, spawning sites, feeding sites,
seasonal wetland or dryland, water
quality or quantity, host species or plant
pollinator, geological formation,
vegetation type, tide, and specific soil
types. Our proposal is intended to
simplify and clarify the process, and to
remove redundancy, without
substantially changing the manner in
which critical habitat is designated. The
Services still expect to provide a
comparable level of detail and
specificity in defining and describing
physical or biological features essential
to the conservation of a species.
Section 424.12(b) describes the
process to be used to identify the
specific areas to be considered for
designation as critical habitat, based on
the statutory definition of ‘‘critical
habitat.’’ With respect to both parts of
the definition, the revised regulations
emphasize that the Secretary will
identify areas that meet the definition
‘‘at a scale determined by the Secretary
to be appropriate.’’ The purpose of this
language is to clarify that the Secretary
cannot and need not make
determinations at an infinitely fine
scale. Thus, the Secretary need not
determine that each square inch, square
yard, acre, or even square mile
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independently meets the definition of
‘‘critical habitat.’’ Nor will the Secretary
necessarily consider legal property lines
in making a scientific judgment about
what areas meet the definition of
‘‘critical habitat.’’ Instead, the Secretary
has discretion to determine at what
scale to do the analysis. In making this
determination, the Secretary may
consider, among other things, the life
history of the species, the scales at
which data are available, and biological
or geophysical boundaries (such as
watersheds), and any draft conservation
strategy that may have been developed
for the species.
Under the first part of the statutory
definition, in identifying specific areas
for consideration, the Secretary must
first identify the geographical area
occupied by the species at the time of
listing. Within the geographical area
occupied by the species, the Secretary
must identify the specific areas on
which are found those physical or
biological features (1) essential to the
conservation of the species, and (2)
which may require special management
considerations or protection.
Under § 424.12(b)(1)(i), the Secretary
will identify the geographical area
occupied by the species using the new
regulatory definition of this term. Under
§ 424.12(b)(1)(ii), the Secretary will then
identify those physical and biological
features essential to the conservation of
the species. These physical or biological
features are to be described at an
appropriate level of specificity, based on
the best scientific data available at the
time of designation. For example,
physical features might include gravel
of a particular size required for
spawning, alkali soil for germination,
protective cover for migration, or
susceptibility to flooding or fire that
maintains early-successional habitat
characteristics. Biological features might
include prey species, forage grasses,
specific kinds or ages of trees for
roosting or nesting, symbiotic fungi, or
a maximum level of nonnative species
consistent with conservation needs of
the listed species. The features may also
be combinations of habitat
characteristics and may encompass the
relationship between characteristics or
the necessary amount of a characteristic
needed to support the life history of the
species. For example, a feature may be
a specific type of forage grass that is in
close proximity to a certain type of
shrub for cover. Because the species
would not consume the grass if there
were not the nearby shrubs in which to
hide from predators, one of these
characteristics in isolation would not be
an essential feature; the feature that
supports the life-history needs of the
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species would consist of the
combination of these two characteristics
in close proximity to each other.
In considering whether features are
essential to the conservation of the
species, the Services may consider an
appropriate quality, quantity, and
spatial and temporal arrangement of
habitat characteristics in the context of
the life-history needs, condition, and
status of the species. For example, a
small patch of meadow may have the
native flowers, full sun, and a
biologically insignificant level of
invasive ants that have been determined
to be important habitat characteristics
that support the life-history needs of an
endangered butterfly. However, that
small patch may be too far away from
other patches to allow for mixing of the
populations, or the meadow may be too
small for the population to persist over
time. So the area could have important
characteristics, but those characteristics
may not contribute to the conservation
of the species because they lack the
appropriate size and proximity to other
meadows with similar characteristics.
Conversely, the exact same
characteristics (native flowers, full sun,
and a biologically insignificant level of
invasive ants), when combined with the
additional characteristics of larger size
and short dispersal distance to other
meadows, may in total constitute a
physical or biological feature essential
to the conservation of the species.
Under § 424.12(b)(1)(iii), the Secretary
will then determine the specific areas
within the geographical area occupied
by the species on which are found those
physical or biological features essential
to the conservation of the species.
Section 424.12(b)(1)(iv) provides for
the consideration of whether those
physical or biological features may
require special management
considerations or protection. In this
portion of the analysis, the Secretary
must determine whether there are any
‘‘methods or procedures useful in
protecting physical and biological
features for the conservation of listed
species.’’ Only those physical or
biological features that may be in need
of special management considerations
or protection are considered further.
The Services may conduct this analysis
for the need of special management
considerations or protection at the scale
of all specific areas, but they may also
do so within each specific area.
The ‘‘steps’’ outlined in
subparagraphs (i) through (iv) above are
not necessarily intended to be applied
strictly in a stepwise fashion. The
instructions in each subparagraph must
be considered, as each relates to the
statutory definition of ‘‘critical habitat.’’
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However, there may be multiple
pathways in the consideration of the
elements of the first part of the
definition of ‘‘critical habitat.’’ For
instance, one may first identify specific
areas occupied by the species, then
identify all features needed by a species
to carry out life-history functions in
those areas through consideration of the
conservation needs of the species, and
then determine which of those specific
areas contain the features essential to
the conservation of the species. The
determination of which features are
essential to the conservation of the
species may consider the spatial
arrangement and quantity of such
features in the context of the life history,
status, and conservation needs of the
species. In some circumstances, not
every location that contains one or more
of the habitat characteristics that a
species needs will be designated as
critical habitat. Some locations may
have important habitat characteristics,
but are too small to support a
population of the species, or are located
too far away from other locations to
allow for genetic exchange. Considered
in context of any generalized
conservation strategy that might be
developed for the species,
§ 424.12(b)(1)(i) through (iv) will allow
for sufficient flexibility to determine
what areas within the geographical area
occupied by the species are needed to
provide for the conservation of the
species.
Occasionally, new taxonomic
information may result in a
determination that a previously listed
species or subspecies is actually two or
more separate entities. In such an
instance, the Services must have
flexibility, when warranted, to continue
to apply the protections of the Act to
preserve the conservation value of
critical habitat that has been designated
for a species listed as one listable entity
(i.e., species, subspecies, or distinct
population segment (DPS)), and which
is being reproposed for listing as one or
more different listable entities (e.g.,
when the Services propose to list two or
more species, subspecies, or DPSs that
had previously been listed as a single
entity). Where appropriate (such as
where the range of an entity proposed
for listing and a previously designated
area of critical habitat align), the
Services have the option to find,
simultaneously with the proposed
listing of the proposed entity or entities,
that the relevant geographic area(s) of
the existing designation continues to
apply as critical habitat for the new
entity or entities. Such a finding
essentially carries forward the existing
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critical habitat (in whole or in part).
Alternatively, the Services have the
option to pursue a succinct and
streamlined notice of proposed
rulemaking to carry forward the existing
critical habitat (in whole or in part),
which draws, as appropriate, from the
existing designation.
More broadly, when applying
§ 424.12(b)(1) to the facts relating to a
particular species, the Services will
usually have more than one option
available for determining what specific
areas constitute the critical habitat for
that species. In keeping with the
conservation-based purpose of critical
habitat, the relevant Service may find it
best to first consider broadly what it
knows about the biology and life history
of the species, the threats it faces, the
species’ status and condition, and,
therefore, the likely conservation needs
of the species with respect to habitat. If
there already is a recovery plan for that
species (which is not always the case
and not a prerequisite for designating
critical habitat), then that plan would be
useful for this analysis.
Using principles of conservation
biology such as the need for appropriate
patch size, connectivity of habitat,
dispersal ability of the species, or
representation of populations across the
range of the species, the Services may
evaluate areas needed for the
conservation of the species. The
Services must identify the physical and
biological features essential to the
conservation of the species and
unoccupied areas that are essential for
the conservation of the species. When
using this methodology to identify areas
within the geographical area occupied
by the species at the time of listing, the
Services will expressly translate the
application of the relevant principles of
conservation biology into the
articulation of the features. Aligning the
physical and biological features
identified as essential with the
conservation needs of the species and
any conservation strategy that may have
been developed for the species allows
us to develop more precise designations
that can serve as more effective
conservation tools, focusing
conservation resources where needed
and minimizing regulatory burdens
where not necessary.
We note that designation of critical
habitat relies on the best available
scientific data at the time of designation.
The Services may not know of, or be
able to identify, all of the areas on
which are found the features essential to
the conservation of a species. After
designation of final critical habitat for a
particular species, the Services may
become aware of or identify other
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features or areas essential to the
conservation of the species, such as
through 5-year reviews and recovery
planning. Newly identified features that
are useful for characterizing the
conservation value of designated critical
habitat can be considered in
consultations conducted under section
7(a)(2) of the Act as part of the best
available scientific and commercial
data. We also note that if there is
uncertainty as to whether an area was
‘‘within the geographical area occupied
by the species, at the time it is listed,’’
the Services may in the alternative
designate the area under the second part
of the definition if the relevant Service
determines that the area is essential for
the conservation of the species.
The second part of the statutory
definition of ‘‘critical habitat’’ (section
3(5)(A)(ii)) provides that areas outside
the geographical area occupied by the
species at the time of listing should be
designated as critical habitat if they are
determined to be ‘‘essential for the
conservation of the species.’’ Section
424.12(b)(2) further describes the factors
the Services will consider in identifying
any areas outside the geographical area
occupied by the species at the time of
listing that may meet this aspect of the
definition of ‘‘critical habitat.’’ Under
§ 424.12(b)(2), the Services will
determine whether unoccupied areas
are essential for the conservation of the
species by considering ‘‘the life-history,
status, and conservation needs of the
species.’’ This will be further informed
by any generalized conservation
strategy, criteria, or outline that may
have been developed for the species to
provide a substantive foundation for
identifying which features and specific
areas are essential to the conservation of
the species and, as a result, the
development of the critical habitat
designation.
Section 424.12(b)(2) subsumes and
supersedes § 424.12(e) of the existing
regulations. Existing section 424.12(e)
provides that the Secretary shall
designate areas outside the
‘‘geographical area presently occupied
by a species’’ only when ‘‘a designation
limited to its present range would be
inadequate to ensure the conservation of
the species.’’ Although the existing
provision represents one reasonable
approach to giving meaning to the term
‘‘essential’’ as it relates to unoccupied
areas, the Services find, based on years
of applying the existing regulations, that
this provision is both unnecessary and
unintentionally limiting. While
Congress supplied two different
standards to govern the Secretary’s
designation of these two types of
habitat, there is no suggestion in the
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legislative history that the Services were
expected to exhaust occupied habitat
before considering whether any
unoccupied area may be essential. In
addition, although section 3(5)(C) of the
Act reflects Congressional intent that a
designation generally should not
include every area that the species can
occupy, this does not necessarily
translate into a mandate to avoid
designation of any unoccupied areas
unless relying on occupied areas alone
would be insufficient. Indeed, there may
be instances in which particular
unoccupied habitat is more important to
the conservation of the species than
some occupied habitat.
For example, a species may occupy at
low densities a large amount of habitat
that is marginal habitat for the species.
That marginal habitat may nonetheless
meet the definition of ‘‘critical habitat’’
because the species has been extirpated
from what historically was superior
habitat, and it is possible to recover the
species if all of the marginal habitat is
thoroughly protected. However, a more
certain and efficient path to recovery
may involve the protection of a
relatively small subset of the marginal
habitat combined with protection of
some of the superior habitat (allowing
for natural expansion or artificial
reintroduction). A variation of this
scenario would involve habitat that may
currently be of high quality, but is
unlikely to remain that way due to the
effects of climate change. Given these
scenarios, it will be useful for the
Services to retain the flexibility to
consider various paths to recovery in
considering what areas to designate as
critical habitat.
We conclude that a rigid step-wise
approach, i.e., first designating all
occupied areas that meet the definition
of ‘‘critical habitat’’ (assuming that no
unoccupied habitat is designated) and
then, only if that is not enough,
designating essential unoccupied
habitat, does not necessarily serve the
best conservation strategy for the
species and, in some circumstances,
may result in a designation that is
geographically larger but less effective
as a conservation tool. Deleting current
§ 424.12(e) will allow us to consider
including occupied and unoccupied
areas in a critical habitat designation
and to follow any general conservation
strategy, criteria, or outline for the
species that may be developed. We
expect that the concurrent evaluation of
occupied and unoccupied areas for a
critical habitat designation will allow us
to develop more precise designations
that can serve as more effective
conservation tools, focusing
conservation resources where needed
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and minimizing regulatory burdens
where not necessary.
In addition, the existing regulatory
provision is unnecessary because the
Secretary in any case must find that the
unoccupied area is ‘‘essential.’’ In many
cases the Secretary may conclude that
an integral part of analyzing whether
unoccupied areas are essential is to
begin with the occupied areas, but the
Act does not require the Services to first
prove that the occupied areas are
insufficient before considering
unoccupied areas. Therefore, we
conclude that deleting existing
§ 424.12(e) restores the two parts of the
statutory definition (for occupied and
unoccupied areas) to the relationship
envisioned by Congress.
As it is currently written, the
provision in § 424.12(e) also confusingly
references present range, while the two
parts of the statutory definition refer to
the area occupied at the time of listing.
In practice, these concepts may be
largely the same, given that critical
habitat ideally should be designated at
or near the time of listing. Nevertheless,
the Services find that it will reduce
confusion to change the regulations to
track the statutory distinction. In
addition, because critical habitat may be
revised at any time, the statutory
distinction may be important during a
revision, which could occur several
years after the listing of the species.
However, we note that unoccupied
areas must be essential for the
conservation of the species, but need
not have the features essential to the
conservation of the species: This follows
directly from the inclusion of the
‘‘features essential’’ language in section
3(5)(A)(i) but not in section 3(5)(A)(ii).
Thus, even keeping in mind that
‘‘features’’ may include features that
support the occurrence of ephemeral or
dynamic habitat conditions, the
Services may identify as areas essential
to the conservation of the species areas
that do not yet have the features, or
degraded or successional areas that once
had the features, or areas that contain
sources of or provide the processes that
maintain essential features in other
areas. Areas may develop features over
time, or, through special management
considerations or protection. The
conservation value may be influenced
by the level of effort needed to manage
degraded habitat to the point where it
could support the listed species. Under
§ 424.12(b)(2), the Services will identify
unoccupied areas, either with the
features or not, that are essential for the
conservation of a species. This section
is intended to provide a flexible, rather
than prescriptive, standard to allow the
Services to tailor the inquiry about what
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is essential to the specific characteristics
and circumstances of the particular
species.
The Services anticipate that critical
habitat designations in the future will
likely increasingly use the authority to
designate specific areas outside the
geographical area occupied by the
species at the time of listing following
any generalized conservation strategy
that might be developed for the species.
As the effects of global climate change
continue to influence distribution and
migration patterns of species, the ability
to designate areas that a species has not
historically occupied is expected to
become increasingly important. For
example, such areas may provide
important connectivity between
habitats, serve as movement corridors,
or constitute emerging habitat for a
species experiencing range shifts in
latitude or altitude (such as to follow
available prey or host plants). Where the
best available scientific data suggest that
specific unoccupied areas are, or it is
reasonable to determine from the record
that they will eventually become,
necessary to support the species’
recovery, it may be appropriate to find
that such areas are essential for the
conservation of the species and thus
meet the definition of ‘‘critical habitat.’’
An example may clarify this situation:
A butterfly depends on a particular host
plant. The host plant is currently found
in a particular area. The data show the
host plant’s range has been moving up
slope in response to warming
temperatures (following the cooler
temperatures) resulting from the effects
of climate change. Other butterfly
species have been documented to have
shifted from their historical ranges in
response to changes in the range of host
plants. Therefore, we rationally
conclude that the butterfly’s range will
likely move up slope, and we would
designate specific areas outside the
geographical area occupied by the
butterfly at the time it was listed if we
concluded this area was essential based
on this information.
Adherence to the process described
above will ensure compliance with the
requirement in section 3(5)(C) of the
Act, which states that, except in those
circumstances determined by the
Secretary, critical habitat shall not
include the entire geographical area
which can be occupied by the
threatened or endangered species.
Existing § 424.12(c) resulted from a
recent separate rulemaking (77 FR
25611; May 1, 2012); it is not addressed
in this rulemaking.
Section 424.12(d) includes minor
language changes and removes the
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example as it is not necessary for the
text of the regulation.
We are removing current § 424.12(e),
as this concept—designating specific
areas outside the geographical area
occupied by the species at the time it is
listed upon a determination by the
Secretary that such areas are essential
for the conservation of the species—is
captured in revised § 424.12(b)(2).
We are redesignating the current
§ 424.12(f) as § 424.12(e) and adding a
second sentence to emphasize that
designation of critical habitat for species
that were listed prior to 1978 is at the
discretion of the Secretaries. The first
sentence of § 424.12(e) provides that the
Secretary ‘‘may designate critical habitat
for those species listed as threatened or
endangered species but for which no
critical habitat has been previously
designated.’’ This is substantially the
same as current § 424.12(f) in the
existing regulations, although the
Services have changed the passive voice
to the active voice.
The new second sentence codifies in
the regulations the principle that the
decision whether to designate critical
habitat for species listed prior to the
effective date of the 1978 Amendments
to the Act (November 10, 1978) is at the
discretion of the Secretary. This
principle is clearly reflected in the text
of the statute and firmly grounded in the
legislative history. The definition of
‘‘critical habitat’’ added to the Act in
1978 provided that the Secretary ‘‘may,’’
but was not required to, establish
critical habitat for species already listed
by the effective date of the 1978
amendments. See Public Law 95–632,
92 Stat. 3751 (Nov. 10, 1978) (codified
at 16 U.S.C. 1532(5)(B)); see also
Conservancy of Southwest Florida v.
United States Fish & Wildlife Service,
No. 2:10–cv–106–FtM–SPC, 2011 WL
1326805, *9 (M.D. Fla. April 6, 2011)
(Florida panther) (plain language of
statute renders designation of habitat for
species listed prior to the 1978
Amendments discretionary), aff’d, 677
F.3d 1073 (11th Cir. 2012); Fund for
Animals v. Babbitt, 903 F. Supp. 96, 115
n.8 (D.D.C. 1995) (grizzly bear) (same).
Similarly, the 1982 amendments
expressly exempted species listed prior
to the 1978 amendments from the
requirement that critical habitat be
designated concurrently with listing.
See Public Law 97–304, 96 Stat. 1411,
sec, 2(b)(4) (Oct. 13, 1982). To reduce
potential confusion, the revised
regulations reflect the discretionary
nature of designations for such species.
As recent litigation has highlighted,
the statutory history regarding the
procedures for undertaking proposals to
designate critical habitat for certain
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7435
species is nuanced and has proven
confusing in other respects as well. For
species listed before passage of the 1982
amendments to the Act (October 13,
1982), any proposed regulations issued
by the Secretary to designate critical
habitat are governed by the provisions
in section 4 of the Act applicable to
proposals to revise critical habitat
designations. This is specified in an
uncodified provision of the 1982
amendments. See Public Law 97–304,
96 Stat. 1411, 1416, 2(b)(2), 16 U.S.C.
1533 (note) (‘‘Any regulation proposed
after, or pending on, the date of the
enactment of this Act to designate
critical habitat for a species that was
determined before such date of
enactment to be endangered or
threatened shall be subject to the
procedures set forth in section 4 of such
Act of 1973 . . . for regulations
proposing revisions to critical habitat
instead of those for regulations
proposing the designation of critical
habitat.’’); see also Center for Biological
Diversity v. FWS, 450 F.3d 930, 934–35
(9th Cir. 2006) (unarmored three-spine
stickleback). While the Services do not
propose to add regulatory text to
address this narrow issue, we explain
below how these provisions must be
understood within the general scheme
for designating critical habitat.
As a result of the above-referenced
provision of the 1982 amendments, final
regulations to designate critical habitat
for species that were listed prior to
October 13, 1982, are governed by
section 4(b)(6)(A)(i) of the Act. By
contrast, for species listed after October
13, 1982, final regulations are governed
by section 4(b)(6)(A)(ii). Proposed rules
for species listed both pre- and post1982 are governed by section 4(b)(5).
Thus, the Services have additional
options at the final rule stage with
regard to a proposal to designate critical
habitat for those species listed prior to
1982 that they do not have when
proposing to designate habitat for other
species. These include an option to
make a finding that the revision ‘‘should
not be made’’ and to extend the 12month deadline by an additional period
of up to 6 months if there is substantial
disagreement regarding the sufficiency
or accuracy of available data. See 16
U.S.C. 1533(b)(6)(B)(i); see also Center
for Biological Diversity, 450 F.3d at 936–
37.
These provisions, however, do not
affect the handling or consideration of
petitions seeking designation of critical
habitat for species listed prior to 1982.
The term ‘‘petition’’ is not used in
section 2(b)(2) of the 1982 amendments
to the Act (compare to section 2(b)(1) of
the same amendments, which mentions
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‘‘[a]ny petition’’ and ‘‘any regulation’’).
Thus, the special procedures for
finalizing proposals to designate critical
habitat for species listed prior to 1982
come into play only upon a decision by
the Secretary to actually propose to
designate critical habitat for such
species. Petitions seeking such
designations are managed just like any
other petition seeking designation,
which are governed by the provisions of
the Administrative Procedure Act rather
than section 4 of the Endangered
Species Act. See 50 CFR 424.14(d);
Conservancy of Southwest Florida, 2011
WL 1326805, at *9 (‘‘It is the Secretary’s
proposal to designate critical habitat
that triggers the statutory and regulatory
obligations, not plaintiffs’ requests that
the Secretary do so.’’); Fund for Animals
v. Babbitt, 903 F. Supp. at 115 (petitions
to designate critical habitat are governed
by the APA, not the ESA).
We are redesignating current
§ 424.12(g) as § 424.12(f) with minor
language changes.
We are redesignating current
§ 424.12(h) as § 424.12(g) with minor
language changes.
We are adding new § 424.12(h). This
paragraph reflects the amendment to
section 4(a)(3)(B)(i) of the Act in the
National Defense Authorization Act for
Fiscal Year 2004 (Pub. L. 108–136).
Section 424.12(h) codifies the
amendments to the Act that prohibit the
Services from designating as critical
habitat lands or other geographic areas
owned or controlled by the Department
of Defense, or designated for its use, if
those lands are subject to an integrated
natural resources management plan
(INRMP) prepared under section 101 of
the Sikes Act (16 U.S.C. 670a), and if the
Secretary determines in writing that
such plan provides a benefit to the
species for which critical habitat is
being designated. In other words, if the
Services conclude that an INRMP
‘‘benefits’’ the species, the area covered
is ineligible for designation. Unlike the
Secretary’s decision on exclusions
under section 4(b)(2) of the Act, this
resulting exemption is not subject to the
discretion of the Secretary (once a
benefit has been found).
Neither the Act nor the National
Defense Authorization Act for Fiscal
Year 2004 defines the term ‘‘benefit.’’
However, the conference report on the
2004 National Defense Authorization
Act (Report 108–354) instructed the
Secretary to ‘‘assess an INRMP’s
potential contribution to species
conservation, giving due regard to those
habitat protection, maintenance, and
improvement projects . . . that address
the particular conservation and
protection needs of the species for
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which critical habitat would otherwise
be proposed.’’ We, therefore, conclude
that Congress intended ‘‘benefit’’ to
mean ‘‘conservation benefit.’’ In
addition, because a finding of benefit
results in an exemption from critical
habitat designation, and given the
specific mention of ‘‘habitat protection,
maintenance, and improvement’’ in the
conference report, we infer that
Congress intended that an INRMP
provide a conservation benefit to the
habitat (e.g., essential features) of the
species, in addition to the species.
Examples of actions that provide
habitat-based conservation benefit to the
species include: Reducing fragmentation
of habitat; maintaining or increasing
populations in the wild; planning for
catastrophic events; protecting,
enhancing, or restoring habitats;
buffering protected areas; and testing
and implementing new habitat-based
conservation strategies.
In the conference report, Congress
further instructed the Secretary to
‘‘establish criteria that would be used to
determine if an INRMP benefits the
listed species.’’ The Services, therefore,
describe in § 424.12(h) some factors that
will help us determine whether an
INRMP provides a conservation benefit:
(1) The extent of area and features
present; (2) the type and frequency of
use of the area by the species; (3) the
relevant elements of the INRMP in terms
of management objectives, activities
covered, and best management
practices, and the certainty that the
relevant elements will be implemented;
and (4) the degree to which the relevant
elements of the INRMP will protect the
habitat from the types of effects that
would be addressed through a
destruction-or-adverse-modification
analysis. FWS will defer to our
Guidelines for Coordination on
Integrated Natural Resource
Management Plans in evaluating these
plans.
Under the Sikes Act, the Department
of Defense is also instructed to prepare
INRMPs in cooperation with FWS and
each appropriate State fish and wildlife
agency. The compliant or operational
INRMP must reflect the mutual
agreement of the involved agencies on
the conservation, protection, and
management of fish and wildlife
resources. In other words, FWS must
agree with an INRMP (reflected by
signature of the plan or letter of
concurrence pursuant to the Sikes Act
(not to be confused with a letter of
concurrence issued in relation to
consultation under section 7(a)(2) of the
Act)) before an INRMP can be relied
upon for making an area ineligible for
designation under section 4(a)(3)(B)(i).
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As part of this process, FWS will also
conduct consultation under section
7(a)(2) of the Act, if listed species or
designated critical habitat may be
affected by the actions included in the
INRMP. Section 7(a)(2) of the Act will
continue to apply to any Federal actions
affecting the species once an INRMP is
compliant or operation. However, if the
area is ineligible for critical habitat
designation under section 4(a)(3)(B)(i),
then those consultations would address
only effects to the species and the
likelihood of the Federal action to
jeopardize the continued existence of
the species.
New § 424.12(h) specifies that an
INRMP must be compliant or
operational to make an area ineligible
for designation under section
4(a)(3)(B)(i). When the Department of
Defense provides a draft INRMP for the
Services’ consideration during
development of a critical habitat
designation, the Services may evaluate
it following the guidelines set forth in
our Policy on Exclusions from Critical
Habitat under Section 4(b)(2) of the Act.
Existing § 424.19 results from a
recent, separate rulemaking (78 FR
53058), and is not addressed in this
rulemaking.
Required Determinations
Regulatory Planning and Review—
Executive Orders 12866 and 13563
Executive Order 12866 provides that
the Office of Information and Regulatory
Affairs (OIRA) in the Office of
Management and Budget will review all
significant rules. The Office of
Information and Regulatory Affairs has
determined that this rule is significant.
Executive Order 13563 reaffirms the
principles of E.O. 12866 while calling
for improvements in the nation’s
regulatory system to promote
predictability, to reduce uncertainty,
and to use the best, most innovative,
and least burdensome tools for
achieving regulatory ends. The
executive order directs agencies to
consider regulatory approaches that
reduce burdens and maintain flexibility
and freedom of choice for the public
where these approaches are relevant,
feasible, and consistent with regulatory
objectives. 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.
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Regulatory Flexibility Act
Under the Regulatory Flexibility Act
(as amended by the Small Business
Regulatory Enforcement Fairness Act
(SBREFA) of 1996; 5 U.S.C. 601 et seq.),
whenever a Federal 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 entities (i.e., small
businesses, small organizations, and
small government jurisdictions).
However, no regulatory flexibility
analysis is required if the head of an
agency, or his designee, certifies that the
rule will 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 a
statement of the factual basis for
certifying that a rule will not have a
significant economic impact on a
substantial number of small entities. We
certified that the proposed rule to
implement these changes to the 50 CFR
part 424 regulations would not have a
significant economic impact on a
substantial number of small entities (79
FR 27066, at 27075). Several
commenters objected to the Services’
determination that a regulatory
flexibility analysis is not required for
this regulation, stating the regulated
community is affected by this
regulation. We explained that NMFS
and FWS are the only entities that are
directly affected by this rule because we
are the only entities that designate
critical habitat, and this rule pertains to
the procedures for carrying out those
designations (See our response to
Comment 81). No external entities,
including any small businesses, small
organizations, or small governments,
will experience any direct economic
impacts from this rule. No information
received during the public comment
period leads us to change our analysis.
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Unfunded Mandates Reform Act (2
U.S.C. 1501 et seq.)
In accordance with the Unfunded
Mandates Reform Act (2 U.S.C. 1501 et
seq.):
(a) On the basis of information
contained in the ‘‘Regulatory Flexibility
Act’’ section above, these regulations
will not ‘‘significantly or uniquely’’
affect small governments. We have
determined and certify pursuant to the
Unfunded Mandates Reform Act, 2
U.S.C. 1502, that these regulations will
not impose a cost of $100 million or
more in any given year on local or State
governments or private entities. A Small
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Government Agency Plan is not
required. As explained above, small
governments will not be affected
because the regulations will not place
additional requirements on any city,
county, or other local municipalities.
(b) These regulations will not produce
a Federal mandate on State, local, or
tribal governments or the private sector
of $100 million or greater in any year;
that is, this rule is not a ‘‘significant
regulatory action’’ under the Unfunded
Mandates Reform Act. These regulations
will impose no obligations on State,
local, or tribal governments.
Takings (E.O. 12630)
In accordance with Executive Order
12630, these regulations will not have
significant takings implications. These
regulations will not pertain to ‘‘taking’’
of private property interests, nor will
they directly affect private property. A
takings implication assessment is not
required because these regulations (1)
will not effectively compel a property
owner to suffer a physical invasion of
property and (2) will not deny all
economically beneficial or productive
use of the land or aquatic resources.
These regulations will substantially
advance a legitimate government
interest (conservation and recovery of
endangered and threatened species) and
will not present a barrier to all
reasonable and expected beneficial use
of private property.
Federalism (E.O. 13132)
In accordance with Executive Order
13132, we have considered whether
these regulations will have significant
Federalism effects and have determined
that a Federalism assessment is not
required. These regulations pertain only
to determinations to designate critical
habitat under section 4 of the Act, and
will not have substantial direct effects
on the States, on the relationship
between the Federal Government and
the States, or on the distribution of
power and responsibilities among the
various levels of government.
Civil Justice Reform (E.O. 12988)
These regulations do not unduly
burden the judicial system and meet the
applicable standards provided in
sections 3(a) and 3(b)(2) of Executive
Order 12988. These regulations will
clarify how the Services will make
designations of critical habitat under
section 4 of the Act.
Government-to-Government
Relationship With Tribes
In accordance with Executive Order
13175 ‘‘Consultation and Coordination
with Indian Tribal Governments,’’ the
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7437
Department of the Interior’s manual at
512 DM 2, and the Department of
Commerce (DOC) Tribal Consultation
and Coordination Policy’’/(May 21,
2013), DOC Departmental
Administrative Order (DAO) 218–8, and
NOAA Administrative Order (NAO)
218–8 (April 2012), we have considered
possible effects of this final rule on
federally recognized Indian Tribes.
Following an exchange of information
with tribal representatives, we have
determined that this rule, which
modifies the general framework for
designating critical habitat under the
ESA, does not have tribal implications
as defined in Executive Order 13175.
We will continue to collaborate/
coordinate with tribes on issues related
to federally listed species and their
habitats and work with them as
appropriate as we develop particular
critical habitat designations, including
consideration of potential exclusion on
the basis of tribal interests. See Joint
Secretarial Order 3206 (‘‘American
Indian Tribal Rights, Federal-Tribal
Trust Responsibilities, and the
Endangered Species Act’’, June 5, 1997).
Paperwork Reduction Act
This rule does not contain any new
collections of information that require
approval by the OMB under the
Paperwork Reduction Act. This rule will
not impose recordkeeping or reporting
requirements on State or local
governments, individuals, businesses, or
organizations. An agency 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.
National Environmental Policy Act
We have analyzed these regulations in
accordance with the criteria of the
National Environmental Policy Act
(NEPA), the Department of the Interior
regulations on Implementation of the
National Environmental Policy Act (43
CFR 46.10–46.450), the Department of
the Interior Manual (516 DM 1–6 and
8)), and National Oceanic and
Atmospheric Administration (NOAA)
Administrative Order 216–6. Our
analysis includes evaluating whether
this action is procedural, administrative,
or legal in nature and, therefore, a
categorical exclusion applies.
Following a review of the changes to
the regulations at 50 CFR 424.01,
424.02, and 424.12 and our
requirements under NEPA, we find that
the categorical exclusion found at 43
CFR 46.210(i) applies to these regulation
changes. At 43 CFR 46.210(i), the
Department of the Interior has found
that the following category of actions
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would not individually or cumulatively
have a significant effect on the human
environment and are, therefore,
categorically excluded from the
requirement for completion of an
environmental assessment or
environmental impact statement:
‘‘Policies, directives, regulations, and
guidelines: that are of an administrative,
financial, legal, technical, or procedural
nature.’’
NOAA Administrative Order 216–6
contains a substantively identical
exclusion for ‘‘policy directives,
regulations and guidelines of an
administrative, financial, legal,
technical or procedural nature.’’
§ 6.03c.3(i).
At the time DOI’s categorical
exclusion was promulgated, there was
no preamble language that would assist
in interpreting what kinds of actions fall
within the categorical exclusion.
However, in 2008, the preamble for a
language correction to this categorical
exclusion gave as an example of an
action that would fall within the
exclusion the issuance of guidance to
applicants for transferring funds
electronically to the Federal
Government. In addition, examples of
recent Federal Register notices invoking
this categorical exclusion include a final
rule that established the timing
requirements for the submission of a
Site Assessment Plan or General
Activities Plan for a renewable energy
project on the Outer Continental Shelf
(78 FR 12676; February 26, 2013), a final
rule that established limited liability for
Noncoal Reclamation by Certified States
and Indian Tribes (78 FR 8822; February
6, 2013), and a final rule changing the
tenure of eagle permits (77 FR 22267;
April 13, 2012). These regulations fell
within the categorical exclusion because
they did not result in any substantive
change. In no way did they alter the
standards for, or outcome of, any
physical or regulatory Federal actions.
The changes to the critical habitat
designation criteria are similar to these
examples of actions that are
fundamentally administrative,
technical, and procedural in nature. The
changes to the regulations at 50 CFR
424.01, 424.02, and 424.12 (except for
paragraph (c)) clarify the procedures
and criteria used for designating critical
habitat, addressing in particular several
key issues that have been subject to
frequent litigation. In addition, the
regulation revisions to 50 CFR 424.01,
424.02, and 424.12 better track the
statutory language of the Act and make
transparent practices the Services follow
as a result of case law. The Services also
make minor wording and formatting
revisions throughout the three sections
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to reflect plain language standards. The
regulation revision as a whole carries
out the requirements of Executive Order
13563 because, in this rule, the Services
have analyzed existing rules
retrospectively ‘‘to make the agencies’
regulatory program more effective or
less burdensome in achieving the
regulatory objectives.’’ None of the
changes to the text of the regulation will
result in changes to the opportunity for
public involvement in any critical
habitat designations.
We also considered whether any
‘‘extraordinary circumstances’’ apply to
this situation, such that the DOI
categorical exclusion would not apply.
See 43 CFR 46.215 (‘‘Categorical
Exclusions: Extraordinary
Circumstances’’). We determined that
no extraordinary circumstances apply.
Although the final regulations would
revise the implementing regulations for
section 4 of the Act, the effects of these
proposed changes would not ‘‘have
significant impacts on species listed, or
proposed to be listed, on the List of
Endangered or Threatened Species or
have significant impacts on designated
Critical Habitat for these species,’’ as
nothing in the revised regulations is
intended to require that any previously
listed species or completed critical
habitat designation be reevaluated on
this basis. Furthermore, the revised
regulations do not ‘‘[e]stablish a
precedent for future action or represent
a decision in principle about future
actions with potentially significant
environmental effects’’ (43 CFR
46.215(e)). None of the extraordinary
circumstances in 43 CFR 46.215(a)
through (l) apply to the revised
regulations in 50 CFR 424.01, 424.02, or
424.12.
Nor would the final regulations trigger
any of the extraordinary circumstances
of NAO 216–6. This rule does not
involve a geographic area with unique
characteristics, is not the subject of
public controversy based on potential
environmental consequences, will not
result in uncertain environmental
impacts or unique or unknown risks,
does not establish a precedent or
decision in principle about future
proposals, will not have significant
cumulative impacts, and will not have
any adverse effects upon endangered or
threatened species or their habitats.
§ 5.05c.
We completed an Environmental
Action Statement for the Categorical
Exclusion for the revised regulations in
50 CFR 424.01, 424.02, and 424.12.
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Energy Supply, Distribution or Use (E.O.
13211)
Executive Order 13211 requires
agencies to prepare Statements of
Energy Effects when undertaking certain
actions. These regulations are not
expected to affect energy supplies,
distribution, and use. Therefore, this
action is a not a significant energy
action, and no Statement of Energy
Effects is required.
References Cited
A complete list of all references cited
in this document is available on the
Internet at https://www.regulations.gov
or upon request from the U.S. Fish and
Wildlife Service (see FOR FURTHER
INFORMATION CONTACT).
Authority
We are taking this action under the
authority of the Endangered Species Act
of 1973, as amended (16 U.S.C. 1531 et
seq.).
List of Subjects in 50 CFR Part 424
Administrative practice and
procedure, Endangered and threatened
species.
Regulation Promulgation
Accordingly, we are amending part
424, subchapter A of chapter IV, title 50
of the Code of Federal Regulations, as
set forth below:
PART 424—[AMENDED]
1. The authority citation for part 424
continues to read as follows:
■
Authority: 16 U.S.C. 1531 et seq.
■
2. Revise § 424.01 to read as follows:
§ 424.01
Scope and purpose.
(a) Part 424 provides regulations for
revising the Lists of Endangered and
Threatened Wildlife and Plants and
designating or revising the critical
habitats of listed species. Part 424
provides criteria for determining
whether species are endangered or
threatened species and for designating
critical habitats. Part 424 also
establishes procedures for receiving and
considering petitions to revise the lists
and for conducting periodic reviews of
listed species.
(b) The purpose of the regulations in
part 424 is to interpret and implement
those portions of the Act that pertain to
the listing of species as threatened or
endangered species and the designation
of critical habitat.
■ 3. Revise § 424.02 to read as follows:
§ 424.02
Definitions.
The definitions contained in the Act
and parts 17, 222, and 402 of this title
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apply to this part, unless specifically
modified by one of the following
definitions. Definitions contained in
part 17 of this title apply only to species
under the jurisdiction of the U.S. Fish
and Wildlife Service. Definitions
contained in part 222 of this title apply
only to species under the jurisdiction of
the National Marine Fisheries Service.
Candidate. Any species being
considered by the Secretary for listing as
an endangered or threatened species,
but not yet the subject of a proposed
rule.
Conserve, conserving, and
conservation. To use and the use of all
methods and procedures that are
necessary to bring any endangered or
threatened species to the point at which
the measures provided pursuant to the
Act are no longer necessary, i.e., the
species is recovered in accordance with
§ 402.02 of this chapter. Such methods
and procedures include, but are not
limited to, all activities associated with
scientific resources management such as
research, census, law enforcement,
habitat acquisition and maintenance,
propagation, live trapping, and
transplantation, and, in the
extraordinary case where population
pressures within a given ecosystem
cannot be otherwise relieved, may
include regulated taking.
Geographical area occupied by the
species. An area that may generally be
delineated around species’ occurrences,
as determined by the Secretary (i.e.,
range). Such areas may include those
areas used throughout all or part of the
species’ life cycle, even if not used on
a regular basis (e.g., migratory corridors,
seasonal habitats, and habitats used
periodically, but not solely by vagrant
individuals).
List or lists. The Lists of Endangered
and Threatened Wildlife and Plants
found at 50 CFR 17.11(h) or 17.12(h).
Physical or biological features. The
features that support the life-history
needs of the species, including but not
limited to, water characteristics, soil
type, geological features, sites, prey,
vegetation, symbiotic species, or other
features. A feature may be a single
habitat characteristic, or a more
complex combination of habitat
characteristics. Features may include
habitat characteristics that support
ephemeral or dynamic habitat
conditions. Features may also be
expressed in terms relating to principles
of conservation biology, such as patch
size, distribution distances, and
connectivity.
Public hearing. An informal hearing
to provide the public with the
opportunity to give comments and to
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permit an exchange of information and
opinion on a proposed rule.
Special management considerations
or protection. Methods or procedures
useful in protecting the physical or
biological features essential to the
conservation of listed species.
Species. Includes any species or
subspecies of fish, wildlife, or plant,
and any distinct population segment of
any vertebrate species that interbreeds
when mature. Excluded is any species
of the Class Insecta determined by the
Secretary to constitute a pest whose
protection under the provisions of the
Act would present an overwhelming
and overriding risk to man.
Wildlife or fish and wildlife. Any
member of the animal kingdom,
including without limitation, any
vertebrate, mollusk, crustacean,
arthropod, or other invertebrate, and
includes any part, product, egg, or
offspring thereof, or the dead body or
parts thereof.
■ 4. In § 424.12, revise paragraphs (a),
(b), and (d) through (h) to read as
follows:
§ 424.12
habitat.
Criteria for designating critical
(a) To the maximum extent prudent
and determinable, we will propose and
finalize critical habitat designations
concurrent with issuing proposed and
final listing rules, respectively. If
designation of critical habitat is not
prudent or if critical habitat is not
determinable, the Secretary will state
the reasons for not designating critical
habitat in the publication of proposed
and final rules listing a species. The
Secretary will make a final designation
of critical habitat on the basis of the best
scientific data available, after taking into
consideration the probable economic,
national security, and other relevant
impacts of making such a designation in
accordance with § 424.19.
(1) A designation of critical habitat is
not prudent when any of the following
situations exist:
(i) The species is threatened by taking
or other human activity, and
identification of critical habitat can be
expected to increase the degree of such
threat to the species; or
(ii) Such designation of critical habitat
would not be beneficial to the species.
In determining whether a designation
would not be beneficial, the factors the
Services may consider include but are
not limited to: Whether the present or
threatened destruction, modification, or
curtailment of a species’ habitat or range
is not a threat to the species, or whether
any areas meet the definition of ‘‘critical
habitat.’’
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7439
(2) Designation of critical habitat is
not determinable when one or both of
the following situations exist:
(i) Data sufficient to perform required
analyses are lacking; or
(ii) The biological needs of the species
are not sufficiently well known to
identify any area that meets the
definition of ‘‘critical habitat.’’
(b) Where designation of critical
habitat is prudent and determinable, the
Secretary will identify specific areas
within the geographical area occupied
by the species at the time of listing and
any specific areas outside the
geographical area occupied by the
species to be considered for designation
as critical habitat.
(1) The Secretary will identify, at a
scale determined by the Secretary to be
appropriate, specific areas within the
geographical area occupied by the
species for consideration as critical
habitat. The Secretary will:
(i) Identify the geographical area
occupied by the species at the time of
listing.
(ii) Identify physical and biological
features essential to the conservation of
the species at an appropriate level of
specificity using the best available
scientific data. This analysis will vary
between species and may include
consideration of the appropriate quality,
quantity, and spatial and temporal
arrangements of such features in the
context of the life history, status, and
conservation needs of the species.
(iii) Determine the specific areas
within the geographical area occupied
by the species that contain the physical
or biological features essential to the
conservation of the species.
(iv) Determine which of these features
may require special management
considerations or protection.
(2) The Secretary will identify, at a
scale determined by the Secretary to be
appropriate, specific areas outside the
geographical area occupied by the
species that are essential for its
conservation, considering the life
history, status, and conservation needs
of the species based on the best
available scientific data.
*
*
*
*
*
(d) When several habitats, each
satisfying the requirements for
designation as critical habitat, are
located in proximity to one another, the
Secretary may designate an inclusive
area as critical habitat.
(e) The Secretary may designate
critical habitat for those species listed as
threatened or endangered but for which
no critical habitat has been previously
designated. For species listed prior to
November 10, 1978, the designation of
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critical habitat is at the discretion of the
Secretary.
(f) The Secretary may revise existing
designations of critical habitat according
to procedures in this section as new
data become available.
(g) The Secretary will not designate
critical habitat within foreign countries
or in other areas outside of the
jurisdiction of the United States.
(h) The Secretary will not designate as
critical habitat land or other geographic
areas owned or controlled by the
Department of Defense, or designated
for its use, that are subject to a
compliant or operational integrated
natural resources management plan
(INRMP) prepared under section 101 of
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the Sikes Act (16 U.S.C. 670a) if the
Secretary determines in writing that
such plan provides a conservation
benefit to the species for which critical
habitat is being designated. In
determining whether such a benefit is
provided, the Secretary will consider:
(1) The extent of the area and features
present;
(2) The type and frequency of use of
the area by the species;
(3) The relevant elements of the
INRMP in terms of management
objectives, activities covered, and best
management practices, and the certainty
that the relevant elements will be
implemented; and
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(4) The degree to which the relevant
elements of the INRMP will protect the
habitat from the types of effects that
would be addressed through a
destruction-or-adverse-modification
analysis.
Dated: January 29, 2016.
Michael J. Bean,
Principal Deputy Assistant Secretary for Fish
and Wildlife and Parks.
Dated: January 29, 2016.
Samuel D. Rauch, III,
Deputy Assistant Administrator for
Regulatory Programs, National Marine
Fisheries Service.
[FR Doc. 2016–02680 Filed 2–10–16; 8:45 am]
BILLING CODE 4310–55–P; 3510–22–P
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Agencies
[Federal Register Volume 81, Number 28 (Thursday, February 11, 2016)]
[Rules and Regulations]
[Pages 7413-7440]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2016-02680]
[[Page 7413]]
Vol. 81
Thursday,
No. 28
February 11, 2016
Part II
Department of the Interior
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Fish and Wildlife Service
Department of Commerce
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National Marine Fisheries Service
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50 CFR Part 424
Listing Endangered and Threatened Species and Designating Critical
Habitat; Implementing Changes to the Regulations for Designating
Critical Habitat; Final Rule
Federal Register / Vol. 81 , No. 28 / Thursday, February 11, 2016 /
Rules and Regulations
[[Page 7414]]
-----------------------------------------------------------------------
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
DEPARTMENT OF COMMERCE
National Marine Fisheries Service
50 CFR Part 424
[Docket No. FWS-HQ-ES-2012-0096; Docket No. 120106025-5640-03;
4500030114]
RIN 1018-AX86; 0648-BB79
Listing Endangered and Threatened Species and Designating
Critical Habitat; Implementing Changes to the Regulations for
Designating Critical Habitat
AGENCY: U.S. Fish and Wildlife Service, Interior; National Marine
Fisheries Service, Commerce.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: We, the U.S. Fish and Wildlife Service (FWS) and the National
Marine Fisheries Service (NMFS) (collectively referred to as the
``Services'' or ``we''), amend portions of our regulations that
implement the Endangered Species Act of 1973, as amended (Act). The
revised regulations clarify, interpret, and implement portions of the
Act concerning the procedures and criteria used for adding species to
the Lists of Endangered and Threatened Wildlife and Plants and
designating and revising critical habitat. Specifically, the amendments
make minor edits to the scope and purpose, add and remove some
definitions, and clarify the criteria and procedures for designating
critical habitat. These amendments are based on the Services' review of
the regulations and are intended to clarify expectations regarding
critical habitat and provide for a more predictable and transparent
critical habitat designation process. Finally, the amendments are also
part of the Services' response to Executive Order 13563 (January 18,
2011), which directs agencies to review their existing regulations and,
among other things, modify or streamline them in accordance with what
has been learned.
DATES: Effective date: This rule is effective March 14, 2016.
Applicability date: This rule applies to rules for which a proposed
rule was published after March 14, 2016.
ADDRESSES: Public input and a list of references cited for this final
rule are available on the Internet at https://www.regulations.gov.
Supporting documentation used in the preparation of this rule will be
available for public inspection, by appointment, during normal business
hours at: U.S. Fish and Wildlife Service, Division of Conservation and
Classification, 5275 Leesburg Pike; Falls Church, VA 22041-0041,
telephone 703/358-2171; facsimile 703/358-1735 and National Marine
Fisheries Service, Office of Protected Resources, 1315 East-West
Highway, Silver Spring, MD 20910, telephone 301-713-1401; facsimile
301-713-0376.
FOR FURTHER INFORMATION CONTACT: Douglas Krofta, U.S. Fish and Wildlife
Service, Division of Conservation and Classification, 5275 Leesburg
Pike, Falls Church, VA 22041, telephone 703/358-2527; facsimile 703/
358-1735; or Marta Nammack, National Marine Fisheries Service, Office
of Protected Resources, 1315 East-West Highway, Silver Spring, MD
20910, telephone 301/427-8469; facsimile 301/713-0376. If you use a
telecommunications device for the deaf (TDD), call the Federal
Information Relay Service (FIRS) at 800-877-8339.
SUPPLEMENTARY INFORMATION: This document is one of three listed below,
of which two are final rules and one is a final policy:
A final rule that amends the regulations governing section
7 consultation under the Endangered Species Act to revise the
definition of ``destruction or adverse modification'' of critical
habitat. The previous regulatory definition had been invalidated by
several courts for being inconsistent with the language of the Act.
That final rule amends title 50 of the Code of Federal Regulations
(CFR) at part 402. The Regulation Identifier Numbers (RINs) are 1018-
AX88 and 0648-BB80, and the final rule may be found on https://www.regulations.gov at Docket No. FWS-R9-ES-2011-0072.
A final rule that amends the regulations governing the
designation of critical habitat under section 4 of the Act. A number of
factors, including litigation and the Services' experiences over the
years in interpreting and applying the statutory definition of
``critical habitat,'' highlighted the need to clarify or revise the
regulations. This final rule (this document) amends 50 CFR part 424. It
is published under RINs 1018-AX86 and 0648-BB79 and may be found on
https://www.regulations.gov at Docket No. FWS-HQ-ES-2012-0096 or at
Docket No. NOAA-NMFS-2014-0093.
A final policy pertaining to exclusions from critical
habitat and how we consider partnerships and conservation plans,
conservation plans permitted under section 10 of the Act, Tribal lands,
national-security and homeland-security impacts and military lands,
Federal lands, and economic impacts in the exclusion process. This
final policy complements the revised regulations at 50 CFR part 424 and
clarifies expectations regarding critical habitat, and provides for a
more predictable and transparent exclusion process. The policy is
published under RIN 1018-AX87 and 0648-BB82 and may be found on https://www.regulations.gov at Docket No. FWS-R9-ES-2011-0104.
Background
The Endangered Species Act of 1973, as amended (16 U.S.C. 1531 et
seq.), states that the purposes of the Act are to provide a means to
conserve the ecosystems upon which listed species depend, to develop a
program for the conservation of listed species, and to achieve the
purposes of certain treaties and conventions. Moreover, the Act states
that it is the policy of Congress that the Federal Government will seek
to conserve threatened and endangered species, and use its authorities
to further the purposes of the Act.
In passing the Act, Congress viewed habitat loss as a significant
factor contributing to species endangerment. Habitat destruction and
degradation have been a contributing factor causing the decline of a
majority of species listed as threatened or endangered species under
the Act (Wilcove et. al. 1998). The present or threatened destruction,
modification, or curtailment of a species' habitat or range is included
in the Act as one of the factors on which to base a determination of
threatened or endangered species status. One of the tools provided by
the Act to conserve species is the designation of critical habitat.
The purpose of critical habitat is to identify the areas that are
essential to the species' recovery. Once critical habitat is
designated, it can contribute to the conservation of listed species in
several ways. Specifying the geographic location of critical habitat
facilitates implementation of section 7(a)(1) of the Act by identifying
areas where Federal agencies can focus their conservation programs and
use their authorities to further the purposes of the Act. Designating
critical habitat also helps focus the conservation efforts of other
conservation partners, such as State and local governments,
nongovernmental organizations, and individuals. Furthermore, when
designation of critical habitat occurs near the time of listing, it
provides a form of early conservation planning guidance (e.g.,
identifying some of the areas that are needed for recovery, the
physical and
[[Page 7415]]
biological features needed for the species' life history, and special
management considerations or protections) to bridge the gap until the
Services can complete recovery planning.
In addition to serving as an educational tool, the designation of
critical habitat also provides a significant regulatory protection--the
requirement that Federal agencies ensure, in consultation with the
Services under section 7(a)(2) of the Act, that their actions are not
likely to destroy or adversely modify critical habitat. The Federal
Government, through its role in water management, flood control,
regulation of resources extraction and other industries, Federal land
management, and the funding, authorization, and implementation of
myriad other activities, may propose actions that are likely to affect
critical habitat. The designation of critical habitat ensures that the
Federal Government considers the effects of its actions on habitat
important to species' conservation and avoids or modifies those actions
that are likely to destroy or adversely modify critical habitat. This
benefit is especially valuable when, for example, species presence or
habitats are ephemeral in nature, species presence is difficult to
establish through surveys (e.g., when a plant's ``presence'' is
sometimes limited to a seed bank), or protection of unoccupied habitat
is essential for the conservation of the species.
The Secretaries of the Interior and Commerce (the ``Secretaries'')
share responsibilities for implementing most of the provisions of the
Act. Generally, marine and anadromous species are under the
jurisdiction of the Secretary of Commerce and all other species are
under the jurisdiction of the Secretary of the Interior. Authority to
administer the Act has been delegated by the Secretary of the Interior
to the Director of FWS and by the Secretary of Commerce to the
Assistant Administrator for Fisheries.
There have been no comprehensive amendments to the Act since 1988,
and no comprehensive revisions to part 424 of the implementing
regulations since 1984. In the years since those changes took place,
the Services have gained considerable experience in implementing the
critical habitat requirements of the Act, and there have been numerous
court decisions regarding the designation of critical habitat.
On May 1, 2012, the Services finalized the revised implementing
regulations related to publishing textual descriptions of proposed and
final critical habitat boundaries in the Federal Register for
codification in the Code of Federal Regulations (77 FR 25611). That
final rule revised 50 CFR 424.12(c) to make the process of designating
critical habitat more user-friendly for affected parties, the public as
a whole, and the Services, as well as more efficient and cost
effective. Since the final rule became effective on May 31, 2012, the
Services have continued the publication of maps of proposed and final
critical habitat designations in the Federal Register, but the
inclusion of any textual description of the designation boundaries in
the Federal Register for codification in the Code of Federal
Regulations is optional. Because we revised 50 CFR 424.12(c)
separately, we do not discuss that paragraph further in this final
rule.
On August 28, 2013, the Services finalized revisions to the
regulations for impact analyses of critical habitat (78 FR 53058).
These changes were made as a result of the President's February 28,
2012, Memorandum, which directed us to take prompt steps to revise our
regulations to provide that the economic analysis be completed and made
available for public comment at the time of publication of a proposed
rule to designate critical habitat. These revisions also state that the
impact analysis should focus on the incremental effects resulting from
the designation of critical habitat. Because we have revised 50 CFR
424.19 separately, we do not discuss that section further in this final
rule.
Summary of Comments and Recommendations
In the proposed rule published on May 12, 2014 (79 FR 27066), we
requested that all interested parties submit written comments on the
proposal by July 11, 2014. We also contacted appropriate Federal and
State agencies, scientific experts and organizations, and other
interested parties, and invited them to comment on the proposal. We did
not receive any requests for a public hearing. We did receive several
requests for an extension of the public comment period, and on June 26,
2014 (79 FR 36284), we extended the public comment period to October 9,
2014. All substantive information provided during the comment periods
has either been incorporated directly into this final determination or
addressed in the more specific response to comments below.
General Issues
(1) Comment: Several commenters, including several States, provided
edits to the proposed regulation.
Our Response: We have reviewed the edits provided and, where
appropriate, we have incorporated them into this final regulation. The
more specific comments and edits are addressed below.
(2) Comment: Several comments stated that the proposed changes to
the regulation would vastly expand the area of critical habitat
designation, in direct conflict with using the critical habitat
designation as a conservation tool.
Our Response: The proposed changes to the regulation are not likely
to vastly expand the areas included in any particular critical habitat
designation. Many commenters focused on the inclusion of unoccupied
areas or perception that the proposed changes expand the Services'
authority to include such areas in a critical habitat designation.
Section 3(5)(A) of the Act expressly allows for the consideration and
inclusion of unoccupied habitat in a critical habitat designation if
such habitat is determined to be essential for the conservation of the
species. However, the existing implementing regulations state that such
unoccupied habitat can be considered only if a determination is made
that the Service(s) cannot recover the species with the inclusion of
only the ``geographical area presently occupied'' by the species, which
is generally understood to refer to habitat occupied at the time of
listing (50 CFR 424.12(e)). As discussed in the proposed rule, we have
determined that the provision is an unnecessary and redundant
limitation on the use of an important conservation tool. Further, we
have learned from years of implementing the critical habitat provisions
of the Act that a rigid step-wise approach, i.e., first designating all
occupied areas that meet the definition of ``critical habitat''
(assuming that no unoccupied habitat is designated) and then, only if
that is not enough, designating essential unoccupied habitat may not be
the best conservation strategy for the species and in some
circumstances may result in a designation that is geographically
larger, but less effective as a conservation tool. Our proposed change
will allow us to consider the inclusion of occupied and unoccupied
areas in a critical habitat designation following any general
conservation strategy that has been developed for the species. In some
cases (e.g., wide ranging species like the spotted owl or lynx), we
have found and expect that we will continue to find that the inclusion
of all occupied habitat in a designation does not support the best
conservation strategy for a species. We expect that the concurrent
evaluation of occupied and unoccupied areas for a
[[Page 7416]]
critical habitat designation will allow us to develop more precise and
deliberate designations that can serve as more effective conservation
tools, focusing conservation resources where needed and minimizing
unnecessary regulatory burdens.
(3) Comment: Several commenters including one State noted that
recovery planning and critical habitat designation are two different
processes. A commenter also asked how the Services will ``infer'' that
unoccupied areas will eventually become necessary for recovery given
that recovery plans do not exist at the time of listing and when it is
not appropriate to designate unoccupied areas that are essential for
recovery.
Our Response: While we agree that the designation of critical
habitat and the recovery planning processes are different and guided by
two separate provisions of the Act and implementing regulations, the
ultimate goal of developing effective conservation tools and measures
to recover a listed species is the same. A general draft conservation
strategy or criterion that informs the construction of a critical
habitat designation is often developed in consultation with staff
working in recovery planning and implementation to ensure
collaboration, consistency, and efficiency as the Services work with
the public and partners to recover a listed species.
We have replaced the word ``infer'' with the word ``determine'' in
our preambular discussion to be clearer. We will determine from the
record and based on any existing conservation strategy for the species
if any unoccupied areas are likely to become necessary to support the
species' recovery. In order to designate unoccupied areas, we are
required by section 3(5)(A) of the Act to determine that such areas are
essential for the conservation of the species.
(4) Comment: Several commenters stated that this attempt by the
Services to expand their own discretion and authority without
congressional authorization is neither justified nor lawful.
Our Response: The amended regulations do not expand the Services'
discretion. Rather, they clarify the existing process by which we
designate critical habitat based on lessons learned over many years of
implementing critical habitat and relevant case law. The amendments
synchronize the language in the implementing regulations with that in
the Act to minimize confusion, and clarify the discretion and authority
that Congress provided to the Secretaries under the Act. The Services
are exercising their discretion to resolve ambiguities and fill gaps in
the statutory language, and the amended regulations are a permissible
interpretation of the statute.
(5) Comment: Several commenters were concerned that the changes
would lead to extensive litigation because the Services failed to
establish clear, measurable, and enforceable criteria for what should
or should not be considered ``habitat'' for a given species, let alone
whether an area should or should not be considered critical habitat
under the Act.
Our Response: The amended regulations do not substantially change
the manner in which critical habitat is designated. Rather, the
amendments primarily clarify how the Services already have been
developing critical habitat designations. We have set forth criteria in
the final rule below. We will also refine, to the extent practicable,
and articulate the specific criteria used for identifying which
features and areas are essential to the conservation of a species and
the subsequent development of a critical habitat designation for each
species (using the best scientific data available) in the proposed and
final critical habitat rules. Our intent is to be more transparent
about how we define the criteria and any generalized conservation
strategy that may have been used in the development of a critical
habitat designation to provide for a more predictable and transparent
critical habitat designation process.
(6) Comment: Several commenters stated that the Services have
misled stakeholders and effectively failed to provide adequate notice
and opportunity for public comment. The comments assert that we should
withdraw our proposal, republish it with a more accurate and clear
summary of the changes to the regulations and their implications, and
provide further opportunity for public comment.
Our Response: The Services have not misled stakeholders. We
initially provided a 60-day public comment period on the proposed
rule.In response to public comments requesting an extension, we
extended the comment period for an additional 90 days. This followed
extensive coordination and discussion with potentially affected Federal
agencies, States, and stakeholders and partners, as well as formal
interagency review under Executive Order 12866. We also held subsequent
calls and extensive webinars with many stakeholders to further inform
them about the proposed rule and address any questions or concerns they
may have had at the time. This satisfies the Services obligation to
provide notice and comment under the Act and the Administrative
Procedure Act (APA).
(7) Comment: Several tribes commented that traditional ecological
knowledge should constitute the best scientific data available and be
used by the Services.
Our Response: Traditional ecological knowledge (TEK) is important
and useful information that can inform us as to the status of a
species, historical and current trends, and threats that may be acting
on it or its habitat. The Services have often used TEK to inform
decisions under the Act regarding listings, critical habitat, and
recovery. The Act requires that we use the best scientific and
commercial data available to inform decisions to list a species and the
best scientific data available to inform designation of critical
habitat, and in some cases TEK may be the best data available. The
Services cannot determine, as a general rule, that TEK will be the best
available data in every rulemaking. However, we will consider TEK along
with other available data, weighing all data appropriately in the
decision process. We will explain the sources of data, the weight given
to various types of data, and how data are used to inform our decision.
Further, any data, including TEK, used by the Services to support a
listing determination or in the development of a critical habitat
designation may be subject to disclosure under the Freedom of
Information Act (FOIA).
(8) Comment: One State strongly advised the Services to withdraw
the Federal Register notice and form a Policy Advisory group on the
issue. The Western Governors' Association requested that the rule be
reworked in cooperation with Western States and utilize State data to
reach a more legally defensible result and to foster partnerships.
Our Response: We appreciate the interest by the State and Western
Governors' Association to form a policy advisory group and work
collaboratively with the Services. However, the Services have already
coordinated with States, Federal agencies, and partners to develop the
amended regulations, and do not agree that a Policy Advisory group is
necessary. The Services have relied on input from States and other
entities, as well as lessons we have learned from implementing the
provisions for critical habitat under the Act, to make the regulations
consistent with the statute, codify our existing practices, and provide
greater clarity and flexibility to designate critical habitat so that
it can be a more effective conservation tool. We will continue
[[Page 7417]]
working collaboratively with Federal, State, and private partners to
ensure that our critical habitat designations are based on the best
available scientific information and balance the conservation needs of
the species with the considerations permitted under section 4(b)(2).
Scope and Purpose (Section 424.01)
(9) Comment: Several commenters including several States suggested
that we retain the words ``where appropriate'' to qualify the reference
to designation or revision of critical habitat as it is a phrase of
limiting potential. Some commenters suggested that we replace the words
with ``unless deemed imprudent'' to better clarify the intention of
this proposed change.
Our Response: As discussed in our proposal, the phrase ``where
appropriate'' was misleading and implied a greater flexibility than the
Services have regarding whether to designate critical habitat. The
Services have the discretion not to designate critical habitat only for
species listed prior to 1978 for which critical habitat has not
previously been designated or where an explicit determination is made
that designation is not prudent. Based on our experiences with
designating critical habitat, a determination that critical habitat is
not prudent is rare. Removing the phrase ``where appropriate'' still
allows the Services to determine that critical habitat is not prudent
for a species if such determination is supported by the best available
scientific information. Replacing it with the phrase ``unless deemed
imprudent'' implies that not prudent determinations are common, which
is not our intent. Deleting ``where appropriate'' provides the
necessary clarification concerning the discretion the Services have in
determining when to designate critical habitat.
(10) Comment: Several commenters suggested that we add the words
``at the appropriate time'' in place of the words ``where appropriate''
to qualify the reference to designation or revision of critical habitat
in Sec. 424.01(a).
Our Response: The Services are required under section 4(a)(3)(A) of
the Act to designate critical habitat, to the maximum extent prudent
and determinable, at the time a species is listed. The inclusion of the
phrase ``at the appropriate time'' and the implication that the
Services have flexibility regarding the timing of the designation
process runs counter to the statutory text.
Definitions
(11) Comment: Several commenters including one State asked us to
keep the definitions for ``critical habitat,'' ``endangered species,''
``plant,'' ``Secretary,'' ``State Agency,'' and ``threatened species''
in the regulation for the purpose of transparency and clarity because
they are core definitions in the authorizing statute and are important
terms in the regulations.
Our Response: These terms are defined in the Act itself, thus
repeating them verbatim in the implementing regulations is redundant
and does not resolve any ambiguity.
(12) Comment: Several commenters were concerned that the addition
of the phrase ``i.e., the species is recovered'' to the definition of
``conserve, conserving, and conservation'' to explain the point at
which the measures provided under the Act are no longer necessary
resulted in a higher standard for conservation than is warranted.
Others commented that the Services are implying that conservation of
critical habitat is equated to meeting recovery goals.
Our Response: The use of ``recovered'' in the definition of
``conserve, conserving, and conservation'' does not introduce a new
standard for conservation. Rather, it clarifies the existing link
between conservation and recovery. Conservation is the use of all
methods and procedures that are necessary to bring any species to the
point at which measures provided by the Act are no longer necessary.
Recovery is improvement in the status of listed species to the point at
which listing is no longer appropriate. Also see our response to
comment 2.
(13) Comment: One commenter stated that if the ``i.e., the species
is recovered'' is added to the definition of ``conserve, conserving,
and conservation,'' then the Services should also add the phrase ``or
extinct'' since these examples describe when the action of conservation
(a set of methods and procedures) are not necessary anymore.
Our Response: ``Conserve, conserving, and conservation'' is defined
in the Act as to use and the use of all methods and procedures which
are necessary to bring any endangered species or threatened species to
the point at which the measures provided pursuant to this Act are no
longer necessary. Extinction does not meet this definition because
extinct species have not been brought to the point at which listing is
no longer necessary. Our regulations at Sec. 424.11(d) state that a
species may be delisted for one or more of the following reasons: (1)
Extinction; (2) Recovery; (3) Original data for classification in
error. Each of these is a separate category, and only recovered species
have reached the recovered state contemplated by the definition of
``conserve, conserving, and conservation.'' (See our response to
comment 12).
(14) Comment: Several commenters stated that proposing to define
``geographical area occupied by the species'' is an amendment to the
definition in the Act and is illegal.
Our Response: The Act does not define the phrase ``geographical
area occupied by the species.'' The Services may develop, clarify, and
revise regulations implementing the provisions of a statute, provided
that our interpretations do not conflict with or exceed the authority
provided by the statute. Since there has been considerable confusion as
to the specific area and scale the phrase refers to, we find that it is
important to provide a reasonable and practicable definition for this
phrase based on what we have learned over the many years of
implementing critical habitat under the Act. Providing this definition
will clarify how we designate critical habitat and which areas are
considered occupied at the time of listing.
(15) Comment: Several States commented that the definition of
``geographical area occupied by the species'' provides no objective
criteria, which will only lead to further confusion and more
litigation. One State requested that we abandon the definition. Several
States offered revised language.
Our Response: The Services are defining the term ``geographical
area occupied by the species'' because the phrase is found in the Act
but is not defined in the Act's regulations, and because there has been
considerable confusion over the proper interpretation of the phrase. We
have clearly stated and explained the definition in our proposal.
Further, we will specify the criteria used for identifying which
features and areas are essential to the conservation of a species and
the subsequent development of a critical habitat designation for each
species (using the best scientific data available) in the proposed and
final rules for a particular critical habitat designation. Our intent
is to be more clear and transparent about how we define the criteria
and any generalized conservation strategy that may have been used in
the development of a critical habitat designation to enhance its use as
a conservation tool.
(16) Comment: One State commented that ``regular or consistent
use'' is a hallmark of a finding of occupied habitat, and should be
required by the
[[Page 7418]]
``geographical area occupied by the species'' definition, not excluded.
The State pointed to the decision in Arizona Cattle Growers' Ass'n v.
Salazar, 606 F.3d 1160 (9th Cir. 2010), in which the court upheld the
application of the Service's definition of occupied habitat for the
Mexican spotted owl as ``areas that the owl uses with sufficient
regularity that it is likely to be present during any reasonable span
of time.'' Another State similarly commented that the use of the term
``even if not used on a regular basis'' in the definition of
geographical area occupied by the species will now enable the Services
to designate critical habitat within areas infrequently used by a
species.
Our Response: We respectfully disagree with the commenter that the
definition of ``geographical area occupied by the species'' should be
limited to only those areas in which the use by the species is
``regular or consistent.'' As discussed at length in our proposal, we
find that the phrase ``geographical area occupied by the species''
should also include areas that the species uses on an infrequent basis
such as ephemeral or migratory habitat or habitat for a specific life-
history phase. We find that this more inclusive interpretation is
consistent with legislative history and Arizona Cattle Growers' Ass'n
v. Salazar, 606 F.3d 1160 (9th Cir. 2010), and congressional intent.
Additionally, based on our experience of implementing the provisions of
critical habitat for many years, we have found that there has been
considerable confusion and differing interpretations of this phrase.
Our intent through the definition provided in our proposal was to
provide greater clarity regarding how we interpret the phrase and the
general scale at which we define occupancy. We give examples in the
rule of areas such as migratory corridors, seasonal habitats, and
habitats used periodically (but not solely by vagrant individuals). We
will use the best scientific data available to determine if such areas
occur for a species. Each species' life cycle is different and the
details of such areas, if they exist, would be explained in the
proposed and final rules designating critical habitat for a particular
species. These areas would also have to meet the criteria for occupied
areas in the definition of critical habitat found in the Act.
(17) Comment: One commenter stated that the definition of
``geographical area occupied by the species'' fails to include
paragraph 3(5)(C) from the Act: ``Except in those circumstances
determined by the Secretary, critical habitat shall not include the
entire geographical area which can be occupied by the threatened or
endangered species.''
Our Response: The regulatory definition is intended to clarify how
we interpret the phrase, not to repeat the language of the statute.
Further, paragraph 3(5)(C) in the Act, applies to the geographic area
that can be occupied by a species, as opposed to the geographic area
actually occupied by the species.
(18) Comment: Several commenters including several States stated
that the definition of ``geographical area occupied by the species''
provides unlimited discretion and authority to the Secretary to
determine the boundaries and size of the critical habitat area.
Our Response: While we agree that the Secretaries are afforded
significant discretion and authority to define and designate critical
habitat, we respectfully disagree with the commenter that the
discretion and authority is unlimited. First, critical habitat is to be
defined and designated based on the best scientific data available.
Second, we have learned from years of implementing the critical habitat
provisions of the Act that often a rigid step-wise approach, i.e.,
first designating all occupied areas that meet the definition of
``critical habitat'' (assuming that no unoccupied habitat is
designated) and then, only if that is not enough, designating essential
unoccupied habitat, may not be the best conservation strategy for the
species and in some circumstances may result in a designation that is
geographically larger, but less effective as a conservation tool. By
providing a definition of ``geographical areas occupied by the
species'' along with the other revisions and clarifications in our
proposal, we can be more precise and deliberate in the development of
our critical habitat designations following any general conservation
strategy that has been developed for the species. Lastly, we are still
bound by paragraph 3(5)(C) (see response to Comment 17 above).
(19) Comment: Several commenters asked, ``What standards will be in
place to substantiate that such areas are used as part of a species'
life cycle and not just an individual vagrant's life cycle'' in the
definition of ``geographical area occupied by the species.'' Several
States also commented that the vagrant animal exception in the rule is
vague and subject to varying interpretations because no definition of
``vagrant'' is provided.
Our Response: As stated in our proposed rule, vagrant individuals
are species who wander far from the known range of the species. We will
use the best scientific data available to determine whether an area is
used by a species for part of its life cycle versus an individual
vagrant's life cycle. The basis for our determination on this point
will be articulated in our proposed and final rules designating
critical habitat for a particular species and subject to public review
and comments, as well as peer review.
(20) Comment: Several commenters suggested that we add the word
``regularly'' to the sentence ``Such areas may include those areas used
regularly throughout all or part of the species' life cycle'' in the
definition of ``geographical area occupied by the species.''
Our Response: The suggested addition would conflict with the second
part of the sentence, in which we state ``even if not used on a regular
basis (e.g., migratory corridors, seasonal habitats, and habitats used
periodically, but not solely by vagrant individuals).'' If the best
scientific data available indicates that these areas are used
periodically during some portion of the listed species' life history,
then these areas should be considered in the development of a critical
habitat designation.
(21) Comment: Several commenters questioned what would happen to
the size, shape, and location of critical habitat areas that were
designated in areas that were not regularly used as conditions change
and travel corridors shift or breeding areas move.
Our Response: As discussed in our proposal and throughout this
final rule, critical habitat is to be based on the best scientific data
available, and to the maximum extent prudent and determinable
promulgated concurrent with the listing of a species. Often at the time
of listing when we are developing a designation of critical habitat for
a species, we may have only limited data concerning the distribution of
the species, its life-history requirements, and other factors that can
inform the identification of features or specific areas essential to
the conservation of the species. Such limited data may still be the
best scientific data available. The Services are required in a proposed
and final designation of critical habitat to clearly articulate what
data are being used and the criteria for defining the specific
essential features and areas. The Services must also allow for public
review and comments on the proposal to ensure public involvement in the
process and provide as much clarity and transparency as possible. The
designation of critical habitat results in a regulation in which the
boundaries of critical habitat for a species are defined. These
boundaries can be changed only
[[Page 7419]]
through rulemaking. Thus, if habitat changes following a designation,
such that those specific areas no longer meet the definition of
``critical habitat,'' the areas within the boundaries of critical
habitat are still critical habitat until such time as a revision to the
designation is promulgated. Any interested party may file a petition
with the Services to request revision of a critical habitat
designation.
(22) Comment: A number of commenters, including several States,
asserted that the proposed definition of ``geographical area occupied
by the species'' is so vague it could lead to huge areas of unoccupied
and potentially unsuitable habitat being designated as critical habitat
that would result in the public or the regulated community having no
consistency.
Our Response: The proposed definition would not lead to more
expansive critical habitat designations. We do not designate areas that
are occupied at the time of listing unless those areas have one or more
of the physical or biological features present that are essential to
the conservation of the species and may require special management
considerations or protection. Any unoccupied habitat at the time of
listing could only be designated critical habitat under section
3(5)(A)(ii) of the Act, which requires a determination by the Secretary
that such areas are essential for the conservation of the species.
Further, we will articulate the specific criteria used for identifying
which features and areas are essential to the conservation of a species
during the subsequent development of a critical habitat designation for
each species (using the best scientific data available) in the proposed
and final rules designating critical habitat for that species. Our
intent is to be more clear and transparent about how we define the
criteria for designation and how in the development of a critical
habitat designation we use any generalized conservation strategy that
may have been developed for the species. The proposed rule would inform
the public, including landowners and businesses, of our critical
habitat designation and allow them time to review and provide comments.
(23) Comment: Two States commented that the Services have justified
the new definition of ``geographical area occupied by the species'' by
misrepresenting the court's decision in Otay Mesa Property L.P. v. DOI,
646 F.3d 914 (D.C. Cir. 2011), reversing 714 F. Supp. 2d 73 (D.D.C.
2010). The States contend that we asserted that the D.C. Circuit's
decision supported our interpretation, even though a thorough review of
the decision reveals the court did not hold or find that the Act allows
the Services to make a post-listing determination of occupancy if based
on adequate data, simply because the court did not decide that
particular issue.
Our Response: We agree that the D.C. Circuit did not hold or find
that the ESA allows the Services to make a post-listing determination
of occupancy. Our proposed rule, however, did not assert that the
circuit court opinion supported our interpretation. Instead, the
proposed rule correctly noted that the district court opinion supported
our interpretation. See 714 F. Supp. 2d at 83 (``The question,
therefore, is not whether FWS knew in 1997, when it listed the San
Diego fairy shrimp as endangered, that there were San Diego fairy
shrimp on Plaintiffs' property but, rather, whether FWS reasonably
concluded, based on data from 2001, that the shrimp had been on the
property in 1997.''). Because that decision was reversed by the D.C.
Circuit, however, we needed to explain what effect that D.C. Circuit's
decision had on the district court opinion with respect to this issue.
Because the D.C. Circuit reversed the district court's opinion on other
grounds (i.e., that the evidence in the record was inadequate), the
D.C. Circuit did not address the interpretive issue of whether later
data can support a determination of occupancy at the time of listing.
Thus, we stated, accurately, that the D.C. Circuit ``did not disagree''
with this aspect of the district court's opinion. We did not mean to
suggest that the D.C. Circuit had considered and affirmed this aspect
of the district court's opinion.
(24) Comment: One State commented that the Service's reliance on
the decision in Arizona Cattle Growers' Assoc. v. Salazar, 606 F.3d
1160 (9th Cir. 2010), to expand the definition of ``occupied'' is
misplaced because the Services oversimplify and misstate the court's
ruling. The State provided additional detail regarding the court's
analysis, noting a variety of factors that the court suggested were
relevant to a case-by-case determination of occupancy, and the court's
emphasis on reasonableness.
Our Response: None of the detail provided by the State is
inconsistent with our summary of the holding: ``a determination that a
species was likely to be temporarily present in the areas designated as
critical habitat was a sufficient basis for determining those areas to
be occupied, even if the species was not continuously present.''
(25) Comment: One commenter asserted that the ``physical or
biological features'' definition has too many if and if/then scenarios
that appear too scientifically attenuated to serve as an appropriate
basis for critical habitat designations.
Our Response: In defining physical and biological features, we
provided examples of types of features and conditions that we have
found to be essential to certain species based on experience over many
years of designating critical habitat for a wide variety of species.
The determination of specific features essential to the conservation of
a particular species will be based on the best scientific data
available and explained in the proposal to designate critical habitat
for that species, which will be available for public comment and peer
review.
(26) Comment: Several States commented that the new definition of
``physical or biological features'' is excessively broad and completely
unnecessary. They stated that the new definition goes too far and
allows the Services to include areas that do not currently have any
essential physical or biological features necessary for a species; they
asserted that the original language of the Act provides enough latitude
to allow for ephemeral, essential habitat requirements. Two States also
asked the Services to more clearly define the phrase ``reasonable
expectation'' found in the preamble discussion (``the Services could
conclude that essential physical or biological features exist in a
specific area . . . if there were documented occurrences of the
particular habitat type in the area and a reasonable expectation of
that habitat occurring again'').
Our Response: Because the term ``physical or biological features''
is not defined in the Act, the Services clarify how they have been
using this term. A ``reasonable expectation'' would be based on the
best scientific data available showing that the habitat has a temporal
or cyclical nature in that in some years particular habitat elements
may not be present, but the record indicates that, once certain
conditions are met, the habitat will recur and be used by the species.
(27) Comment: One State contended that the Services support the new
definition of ``physical or biological features'' with a flawed
interpretation of the opinion in Cape Hatteras Access Preservation
Alliance v. DOI, 344 F. Supp. 2d 108 (D.D.C. 2004). According to the
State: That opinion does not justify expanding the meaning and breadth
of the phrase; the Services should withdraw the definition because the
Services cite no authority for making
[[Page 7420]]
such a change and thus lack any justification for doing so; the Court
explicitly rejected the Service's attempt to broaden the scope of
critical habitat designation; and the Services should not attempt to
expand their authority by circumventing the Federal courts.
Our Response: The district court rejected the U.S. Fish and
Wildlife Service's critical habitat designation for the piping plover
as including lands that did not currently contain the features defined
in the rule, but noted that it was not addressing whether dynamic land
capable of supporting plover habitat can itself be one of the physical
or biological features essential to the conservation of the plover. The
court noted that the Service had not made that assertion in the context
of the piping plover designation. To address this unintentional gap, we
are setting out our interpretation as part of the framework
regulations. This new definition clarifies that features can be dynamic
or ephemeral habitat characteristics. We clearly state in the rule that
an area within the geographical area occupied by the species, with
habitat that is not ephemeral by nature but that has been degraded in
some way, must have one or more of the features at the time of
designation to be critical habitat.
(28) Comment: Several commenters recommended that the Services
separately define ``physical features'' and ``biological features'' to
provide greater clarity.
Our Response: The Act refers to ``physical or biological
features,'' so it is not necessary to define them separately. We find
that the definition provided in the draft proposal along with the
examples and accompanying explanation provides sufficient clarity and
that separately defining these terms in the final regulation would not
be helpful. However, the Services must clearly articulate, in proposed
and final rules designating critical habitat for a particular species,
which physical or biological features are essential to the conservation
of the species and the basis for that critical habitat.
(29) Comment: Several commenters suggested that we remove ``at a
scale determined by the Secretary to be appropriate'' and add ``for a
specific unoccupied area to be designated as critical habitat, it must
be reasonably foreseeable that (1) such area will develop the physical
and biological features necessary for the species and (2) such features
will be developed in an amount and quality that the specific area will
serve an essential role in the conservation of the species.''
Our Response: We determine whether unoccupied areas are essential
for the conservation of the species by considering the best available
scientific data regarding the life-history, status, and conservation
needs of the species, which include considerations similar to those
raised by the commenter. However, we do not agree that the specific
findings suggested by the commenter either are required under the
statute or are useful limitations for the Services to impose on
themselves. Further, our rationale for why unoccupied areas are
essential for the conservation of the species will be articulated in
the proposed rule designating critical habitat for a particular species
and available for public review and comment. Finally, we decline to
remove the language ``at a scale determined by the Secretary to be
appropriate because we have concluded that it is useful to clarify that
different circumstances will require different scales of analysis, and
the Secretary retains the discretion to choose an appropriate scale.
(30) Comment: A commenter suggested that we add the phrase ``based
on the best scientific data available'' after the word ``appropriate''
in ``the Secretary will identify, at a scale determined by the
Secretary to be appropriate'' in Sec. 424.12(b)(2). The commenter
further stated that this provides a reference to the scientific basis
on which the Secretary will determine this scale.
Our Response: The phrase ``based on the best scientific data
available'' is captured in Sec. 424.12(b)(1)(ii). Under section
4(b)(2) of the statute, it also states that the Secretary shall
designate critical habitat, and make revisions thereto, under
subsection (a)(3) on the basis of the best scientific data available.
It would be redundant to add the phrase to the section the commenter
has suggested. Nevertheless, as stated above, the Secretary's choice of
scale will be based on the best available scientific data.
(31) Comment: A commenter suggested that we replace the phrase
``conservation needs of the species'' with ``physical or biological
features'' in Sec. 424.12(b)(2). The commenter stated that the phrase
``conservation needs of the species'' is undefined and adds ambiguity
to the regulation.
Our Response: Section 424.12(b)(2) refers to the designation of
critical habitat in unoccupied areas. Under section 3(5)(A)(ii) of the
statute, unoccupied areas are subject only to the requirement that the
Secretary determine that such areas are essential for the conservation
of the species. The presence of physical or biological features is not
required by the statute for the inclusion of unoccupied areas in a
designation of critical habitat. Incorporating the edit suggested by
the commenter would limit Secretarial discretion in a way inconsistent
with the statute by mandating the presence of essential features as a
prerequisite to inclusion of unoccupied areas in a critical habitat
designation. Therefore, it would be inappropriate to use the term
``physical or biological features'' in this section.
(32) Comment: Several commenters stated that the Services' claim
that they may designate acres or even square miles without evidence
that those areas contain features essential to the conservation of the
species is contrary to the Act. Two States commented that the scale of
critical habitat should not be left to the Secretary's absolute
discretion and must be chosen and justified at a scale that both makes
sense in terms of the habitat needs of the species and is fine enough
to demonstrate that the physical or biological features are found in
each specific area of occupied habitat. One State also provided revised
language for Sec. 424.12(b)(1) by replacing ``at a scale determined by
the Secretary to be appropriate'' with ``at a scale consistent with the
geographical extent of the physical or biological features essential to
the species' conservation.''
Our Response: We state in the proposed regulation that the
Secretary need not determine that each square inch, yard, acre, or even
mile independently meets the definition of critical habitat. However,
setting out defined guidelines for the scale of an analysis in
regulations would not be practicable for the consideration of highly
diverse biological systems and greatly differing available data. Each
critical habitat designation is different in terms of area proposed,
the conservation needs of the species, the scope of the applicable
Federal actions, economic activity, and the scales for which data are
available. Additionally, the scale of the analysis is very fact
specific. Therefore, the Services must have flexibility to evaluate
these different areas in whatever way is most biologically and
scientifically meaningful. For example, for a narrow-endemic species, a
critical habitat proposal may cover a small area; in contrast, for a
wide-ranging species, a critical habitat proposal may cover an area
that is orders of magnitude greater. The appropriate scale for these
two species may not be the same. For the narrow-endemic species, we may
look at a very fine scale with a great level of detail. In contrast,
for the wide-ranging
[[Page 7421]]
species, which may cover wide expanses of land or water, we may use a
coarser scale, due to the sheer size of the proposed designation. Each
critical habitat proposal includes a description of the scope of the
area being proposed, and uses a scale appropriate to that situation
based on the best scientific data available. The suggested language
would not allow for the Secretarial discretion that is needed to be
flexible to meet the conservation needs of the species. The proposed
rule designating critical habitat for a particular species is made
available for public review and comment, and interested parties may
comment on the scale for a specific designation.
(33) Comment: Several commenters stated that, in reaching this
determination, the Services appear to conflate disparate terminology
(specific areas versus occurrences) and rely upon a vague term (range)
that does not adequately delineate what geographic areas are actually
occupied by a species. Several commenters also requested additional
explanation of the term ``range.''
Our Response: Under section 3(5)(A)(i) of the Act, specific areas
designated as critical habitat include those specific areas within the
geographical area occupied by the species at the time the species is
listed. As discussed in our proposal and this final rule, the
geographical area that may generally be delineated around the species'
occurrences is synonymous with the species' range. The term ``range''
used in our proposal refers to the general area currently occupied by
the species at the time the listing determination is made. These areas
are occupied by the species throughout all or part of the species' life
cycle, even if not used on a regular basis. Some examples we give are
migratory corridors, seasonal habitats, and habitats used periodically,
but not solely by vagrant individuals. This scale of occupancy is
different from a very narrow or limited delineation of areas of
occupancy identified through presence and absence surveys for localized
occurrences of the species. We, therefore, disagree that we are using a
vague term in referring to range.
(34) Comment: Several commenters including one State stated that by
defining the geographical area occupied by the species as coextensive
with the ``range'' and including multiple areas of occurrence, the
Services are expanding the geographic extent of occupied habitat beyond
the limits of judicial interpretation. They suggested we should define
the area occupied by the species as limited to the specific location
where the species occurs on a regular or consistent basis.
Our Response: We have indicated that the geographical area occupied
by the species is likely to be larger than the specific areas that
would then be analyzed for potential designation under section
3(5)(A)(i). We are not suggesting that the specific areas included in
critical habitat should fill this area. To limit the definition to
specific locations where the species occurs on a regular or consistent
basis would not allow the Secretaries to designate areas that may be
important for the conservation of a listed species that may only be
periodically used by a species, such as breeding areas, foraging areas,
and migratory corridors, thereby limiting Secretarial discretion.
(35) Comment: One State asked if the range in the geographical area
occupied by the species definition refers to the historical range or
the currently occupied range.
Our Response: The term ``range'' as indicated in our proposal
refers to the generalized area currently occupied by the species at the
time the listing determination is made, not the historical range.
(36) Comment: One State also wanted to know if land-use
restrictions within the geographical area occupied by the species would
be put into place in addition to the designated critical habitat.
Our Response: The revised regulations would not result in any
change to land-use restrictions beyond the existing regulatory
requirements under section 7 of the Act that Federal agencies consult
with the Services to ensure that the actions they carry out, fund, or
authorize are not likely to destroy or adversely modify critical
habitat (see the final rule published elsewhere in today's Federal
Register). The Act provides no special regulatory protections for those
areas within the geographic area occupied by the species that are not
designated as critical habitat, although the section 7 prohibition on
jeopardy and the section 9 prohibitions may still be applicable.
(37) Comment: Several States disagree with the Services'
interpretation of the definition of ``occupied.'' This interpretation
and inclusion of ``periodic or temporary'' areas will lead to a much
larger consideration of critical habitat that is largely unnecessary
for species recovery.
Our Response: Identifying the geographic area occupied at the time
of listing is only the first step in designating critical habitat. In
occupied areas, we can only designate critical habitat if one or more
of the physical or biological features are present and are found to be
essential to the conservation of the species and may require special
management considerations or protection. The inclusion of periodic or
temporary areas would be based on the best scientific data available
for the species and these areas would have to meet the criteria above.
(38) Comment: Several commenters asked what constitutes being
``temporarily present?'' The Services should explain that occupied
areas require a demonstration of regular or consistent use within a
reasonable period of time. One State commented that the Services should
clarify the meaning of the terms ``periodically'' and ``temporarily''
to provide adequate guidance and set reasonable limits for potential
critical habitat designations.
Our Response: We will use the best scientific data available to
determine occupied areas including those that are used only
periodically or temporarily by a listed species during some portion of
its life history. This will be determined on a species-by-species
basis, and our rationale would be explained in the proposed and final
rules for these species, which would be available for public review and
comment.
(39) Comment: Several commenters, including two States, were
concerned about using ``indirect or circumstantial'' evidence to
determine occupancy and questioned whether this qualified as the best
scientific data available. One of the commenters asserted that the
Services should only designate areas as occupied based on scientific
evidence (including traditional and local knowledge) that breeding,
foraging, or migratory behaviors actually occur in that location on a
regular or consistent basis.
Our Response: The Services will rely on the best scientific data
available in determining which specific areas were occupied at the time
of listing and which of these contain the features essential to the
conservation of the species. The best available scientific data in some
cases may only be indirect or circumstantial evidence. We will explain
in the proposed rule designating critical habitat for a particular
species if and how such evidence was used to determine occupancy and
will provide the public with an opportunity to review and comment.
(40) Comment: Several commenters, including two States, asked us to
define and explain ``life-history needs.''
Our Response: We give a sample list of life-history needs in the
rule. This list includes but is not limited to water characteristics,
soil type, geological features, sites, prey, vegetation, symbiotic
species, or other features. The
[[Page 7422]]
life-history needs are what the species needs throughout its different
life stages to survive and thrive.
(41) Comment: One State commented that the term ``sites'' in the
definition of ``physical or biological features'' is wholly ambiguous
and must be defined, explained, or deleted.
Our Response: We included the term ``sites'' in the definition of
physical or biological features to keep the same level of specificity
as currently is called for in the regulations, and our current
regulations list ``sites for breeding, reproduction, rearing of
offspring, germination, or seed dispersal'' among the examples of
primary constituent elements that might be specified (50 CFR
424.12(b)(4)). The term ``sites'' does not need to be defined or
further explained because we rely on a plain dictionary meaning of
``site'': The place, scene, or point of an occurrence or event
(Merriam-Webster, 2015).
(42) Comment: One State suggested that we simplify the ``physical
or biological features'' definition as follows: ``Geographic or
ecological elements within a species' range that are essential to its
survival and reproduction, whether single or in combination, or
necessary to support ephemeral habitats. Features may be described in
conservation biology terms, including patch size and connectivity.''
Our Response: We appreciate the State providing edits to simplify
the phrase; however, based on our years of experience designating
critical habitat and implementing it, we find that the text in our
proposal and this final rule will provide greater clarity.
(43) Comment: Several commenters, including one State, indicated
that we needed a more specific delineation of what features may be
considered and how they relate to the needs of the species.
Our Response: We respectfully disagree with the commenters that
further clarification should be added in this revised regulation.
However, we do agree that we need to clearly articulate in our proposed
and final rules designating critical habitat for each species how the
essential features relate to the life-history and conservation needs of
the species. This type of specificity will be in the individual
proposed and final rules designating critical habitat for each species.
As is our general practice, we will clearly lay out the features and
how they relate to the needs of the species in each rule.
(44) Comment: Several commenters asked us to clarify the
distinction, if any, between features that support the life-history
needs of the species and features that are essential to the
conservation of the species.
Our Response: Our definition of physical or biological features is
the first step, and we do not assume that all features are essential.
In many circumstances the features that support life-history needs of
the species are the features that are essential to the conservation of
the species. The features that are essential to the conservation of the
species are those found in the appropriate quality, quantity, and
spatial and temporal arrangements in the context of the life history,
status, and conservation needs of the species. This varies according to
the species. For example, for a small, endemic species the features
that support the life-history needs may be essential themselves, but
for a wide-ranging species what rises to the level of essential
features may rely more on the quality, quantity, and arrangement of
those features.
(45) Comment: Several commenters sought an explanation for how the
requisite physical and biological features would be identified,
documented, and verified during the critical-habitat-designation
process.
Our Response: We use the best scientific data available to
determine the life-history needs of the species. The essential physical
or biological features support the life-history and conservation needs
of the species. A description of the essential features for each
species and how they relate to its life-history and conservation needs
will be articulated in the proposed and final rules designating
critical habitat for a particular species. This description of the
essential features, as well as the designation that is based on them,
will be available for public review and comment during the rulemaking
process.
(46) Comment: Several commenters stated that the description of the
relevant features cannot be in broad terms, but must be specific enough
to limit critical habitat to the most ``essential areas'' and help
provide an understanding of what the species actually requires to
return from the brink of extinction.
Our Response: When evaluating occupied habitat, we agree that the
statute requires us to determine which areas contain physical or
biological features essential to the conservation of the species (that
may require special management considerations or protection). In every
proposed and final rule designating critical habitat for a particular
species, we describe those features that we have determined to be
essential and explain the basis for our determination. However, we
respectfully disagree that broadly described features are necessarily
inappropriate. The level of specificity in our description of the
features is primarily determined by the state of the best scientific
information available for that species. We will provide as much
specificity as is appropriate in light of what is known about the
species' habitat needs, while recognizing that the available science
may still be evolving for that species. Where the available information
is still evolving, it may not be possible or necessary to provide a
high level of specificity, and it may frustrate the conservation
purposes of the Act to attempt to do so. See Arizona Cattle Growers'
Ass'n v. Kempthorne, 534 F. Supp. 2d 1013, 1025 n.2 (D. Ariz. 2008),
aff'd sub nom. Arizona Cattle Growers' Ass'n v. Salazar, 606 F.3d 1160
(9th Cir. 2010).
Finally, we must disagree with the commenter's suggestion that in
identifying essential features the Services must identify what the
species' actually requires to return from ``the brink of extinction.''
Critical habitat is generally required for threatened species as well
as endangered species. Moreover, the Services are not required to have
developed a recovery plan prior to designating critical habitat for any
species. Home Builders Ass'n of Northern Cal. v. U.S. Fish and Wildlife
Service, 616 F.3d 983, 989-90 (9th Cir. 2010). Our determinations of
which features are ``essential'' thus depend on an understanding of the
species' habitat needs rather than on a specific projection of how the
species could be recovered.
(47) Comment: Several commenters stated that the plain language of
the Act limits the scope of any designated area to those features
essential to the species, and does not authorize the designation of
areas that may include those subsidiary characteristics that are
essential for the development of the features themselves.
Our Response: We respectfully disagree and interpret the statutory
language not to limit ``features'' to those habitat characteristics
that make habitat immediately usable by the species. In other words,
the physical or biological features referred to in the definition of
``critical habitat'' can include features that allow for the periodic
development of habitat characteristics immediately usable by the
species. An interpretation of ``features'' that referred only to
immediately usable habitat would render many essential areas ineligible
for designation as critical habitat, thwarting Congress's intent that
designation of critical habitat should contribute to species'
conservation.
[[Page 7423]]
We will use the best scientific data available to identify features
essential to the conservation of the species and clearly identify how
they relate to the life-history and conservation needs of the species.
When considering what features are essential, it is sometimes necessary
to allow for the dynamic nature of the habitat, such as successional
stages of habitat, which could consist of old-growth habitat or habitat
newly formed through disturbance events such as fire or flood events.
Thus, the physical or biological features essential to the conservation
of the species may include features that support the occurrence of
ephemeral or dynamic habitat conditions. The example we gave in the
proposed rule was a species that may require early-successional
riparian vegetation in the Southwest to breed or feed. Such vegetation
may exist only 5 to 15 years after a local flooding event. The
necessary features, then, may include not only the suitable vegetation
itself, but also the flooding events, topography, soil type, and flow
regime, or a combination of these characteristics and the necessary
amount of the characteristics that can result in the periodic
occurrence of the suitable vegetation. The flooding event would not be
a subsidiary characteristic as suggested by the commenter, but would
itself be a feature necessary for the vegetation to return. So in this
case, it would be a combination of features, flooding, and vegetation
that would be necessary to the conservation of the species.
(48) Comment: Several commenters, including two States, were
concerned that designating critical habitat based on the presence of
certain characteristics that may be necessary to eventually support the
periodic occurrence of riparian vegetation, without evidence that the
vegetation would actually develop, constitutes an impermissible
reliance upon hope and speculation. They further stated that the
Services must go through a separate inquiry determining why it is
reasonably foreseeable to conclude that the potential critical habitat
will develop the physical or biological features at some point in the
future.
Our Response: We will use the best scientific data available to
support the identification of features essential to the conservation of
the species and clearly identify how they relate to the life-history
and conservation needs of the species. When considering what features
are essential, it is sometimes necessary to allow for the dynamic
nature of the habitat, such as successional stages of habitat, which
could consist of old-growth habitat or habitat newly formed through
disturbance events such as fire or flood events. This does not
constitute reliance on mere hope or speculation but is based on an
understanding of the relevant ecological processes. We also disagree
with the characterization of this situation as involving ``potential
critical habitat'' that ``will develop the physical or biological
features at some point in the future.'' Properly understood, the
essential features would currently exist in these areas, even though
they may not be currently manifesting the shorter-term habitat
conditions immediately usable by the species. Such areas may currently
meet the definition of ``critical habitat'' and not be merely
``potential critical habitat.''
(49) Comment: Several commenters stated that the Services' position
that ``most circumstances'' require ``special management'' is
inconsistent with congressional intent to narrow the definition of
``critical habitat'' to require a very careful analysis of what is
actually needed for survival of the species. Several commenters,
including two States, also indicated that the Services must continue to
make the factual determination that special management is needed as
required by the Act.
Our Response: We make the determination and describe the special
management considerations or protections that may be needed in the
proposed and final rules designating critical habitat for each critical
habitat area. However, it has been our experience that, in most
circumstances, the physical or biological features essential to the
conservation of endangered species may require special management
considerations or protection in all areas in which they occur. This is
particularly true for species that have significant habitat-based
threats, which is the case for most of our listed species. The statute
directs us to identify the essential physical or biological features
which ``may require'' special management considerations or protection,
a standard that suggests we should be cautious and protective. We do
acknowledge that if in some areas the essential features clearly do not
require special management considerations or protection, then that area
does not meet this part (section 3(5)(A)(i)) of the definition of
``critical habitat.'' However, we expect based on our experience with
designating critical habitat that these circumstances will be rare. In
our proposed and final critical habitat rules, we will continue to make
factual determinations as to whether special management considerations
or protection may be required.
(50) Comment: Several States commented that the new interpretation
of ``special management considerations or protection'' set out in the
preamble appears to presume that areas covered by existing protection
plans will actually be more likely to be designated as critical
habitat, and could act as a disincentive to implementing voluntary pre-
designation conservation initiatives, in direct contravention to recent
Services' policies attempting to incentivize voluntary conservation.
Our Response: We respectfully disagree. We are directed by the Act
to identify areas that meet the definition of ``critical habitat''
(i.e., occupied areas that contain the essential physical or biological
features that may require special management considerations or
protection and unoccupied areas that are essential for the conservation
of a species) without regard to land ownership. We also make the
determination and describe the special management considerations or
protections that may be needed in the proposed and final rules for each
critical habitat area. The consideration of whether features in an area
may require special management considerations or protection occurs
independent of whether any form of management or protection occurs in
the area. This does not preclude the Services from considering the
exclusion of these areas under section 4(b)(2) of the Act based on
conservation programs, plans, and partnerships prior to issuing the
final critical habitat rule.
(51) Comment: Several commenters stated that the Services cannot
designate critical habitat based on the general assertions that the
area contains the essential physical or biological features. Instead,
the Services must demonstrate that the relevant features are found
within a specific area.
Our Response: In the first part of the definition of ``critical
habitat'' in the Act, we are required to identify specific areas within
the geographical area occupied by the species at the time it is listed
on which are found those physical or biological features essential to
the conservation of the species and which may require special
management considerations or protection. In our proposed and final
critical habitat rules, we identify which features occur in the area,
the basis on which we are identifying them as essential features,
including how they provide for the life-history and conservation needs
of the species, and whether they may require special management
considerations or
[[Page 7424]]
protection. These rules will be available for public review and
comment.
(52) Comment: Several commenters suggested that we remove
``principles of conservation biology'' from the definition of
``physical and biological features.''
Our Response: We respectfully disagree. The sentence ``Features may
also be expressed in terms of relating to principles of conservation
biology, such as patch size, distribution distances, and connectivity''
explains more clearly how we may identify the features. The principles
of conservation biology are generally accepted among the scientific
community and consistently used in species-at-risk status assessments
and development of conservation measures and programs.
(53) Comment: Several commenters requested that we add language
delineating the area ``around'' the species occurrences, either by
using a distance or a reference to the species' natural functions in
the geographic area definition.
Our Response: We are unable to determine a universal distance or a
reference to the species' natural functions that would be applicable to
all species. This analysis and determination is best left to the
specific critical habitat rulemaking for a given species. In those
proposed and final rules, we can be specific for each species based on
its life-history needs and more precisely define the geographical area
occupied by the species. The rules will be available for public review
and comment.
(54) Comment: Several commenters, including one State, indicated
that the proposed Sec. 424.12(b)(2) and deletion of current Sec.
424.12(e) would relieve the Services of any requirements that they
justify the designation of unoccupied habitat by demonstrating the
inadequacies of occupied habitat for the conservation of the species.
They further stated that this was a major departure in the law
regarding designation of critical habitat.
Our Response: We respectfully disagree. The proposed rule clearly
explains that the Act does not require the Services to first prove that
the occupied areas are insufficient before considering unoccupied
areas. The regulatory provision at 424.12(e) merely restated the
requirement from the statutory definition in a different way. We will
still explain based on the best scientific data available, why the
unoccupied areas are essential for the conservation of the species.
(55) Comment: Several commenters pointed out that we use ``no
longer necessary'' in the new definition of ``conserve, conserving, and
conservation'' and the words ``no longer appropriate'' in the
definition of ``recovery'' in 50 CFR 402.02. The commenters asserted
that these are two different standards and that we should pick one of
them.
Our Response: The words ``no longer necessary'' are used in the
statutory definition of ``conserve, conserving, and conservation'' in
the Act. The rule simply points out that the concept described in the
statutory language is equivalent to ``recovery.'' That term is defined
in Sec. 402.02, which we are not revising at this time.
(56) Comment: Several commenters stated that the National Marine
Fisheries Service's interpretation of the phrase ``which interbreeds
when mature'' was upheld by the Ninth Circuit in Modesto Irr. Dist. v.
Gutierrez, 619 F.3d 1024 (9th Cir. 2010), and that the Act also
requires that a group of organisms must interbreed when mature to
qualify as a distinct population segment (DPS), which is in contrast to
the Services' interpretation of the phrase in the proposed rule.
Our Response: We respectfully disagree that our interpretation of
``interbreeds when mature'' is at odds with the ruling in Modesto
Irrigation District. In that case, the Ninth Circuit did not hold that
actual interbreeding among different populations is required in order
to include such populations in a single DPS. To the contrary, the court
made it clear that Congress did not intend to create a ``rigid
limitation'' on the Services' discretion to define DPSs. On the
``narrow issue'' of whether the ESA or the DPS Policy required that
NMFS place interbreeding steelhead and rainbow trout in the same DPS,
the court deferred to NMFS's judgment that there was no such
requirement. Id. at 1037. While NMFS did state in the challenged rule
that ``[t]he ESA requirement that a group of organisms must interbreed
when mature to qualify as a DPS is a necessary but not exclusive
condition'' (71 FR 834, 838 (Jan. 5, 2006)), nothing in the rule
suggested that NMFS's position was that actual interbreeding among
disparate populations was required, and that biological capacity to
interbreed would not be sufficient.
(57) Comment: Several commenters stated that the Services did in
fact revise the regulations in our discussion of ``interbreeds when
mature'' by inserting the phrase ``A distinct population segment
``interbreeds when mature'' when it consists of members of the same
species or subspecies in the wild that are capable of interbreeding
when mature'' to the definition of a ``species.'' They further stated
that this was an Administrative Procedure Act violation and that the
phrase should be removed in the final rule.
Our Response: The commenters are correct that we proposed to amend
the definition of ``species.'' In the preamble we wrote, ``Finally, we
explain our interpretation of the meaning of the phrase `interbreeds
when mature,' which is found in the definition of `species.' . . .
Although we are not proposing to revise the regulations at this time,
we are using this notice to inform the public of our longstanding
interpretation of this phrase.'' Our intent was to explain how we have
interpreted the phrase, but by inadvertently including this
interpretation in the regulatory language of the proposed rule, we in
fact were proposing to change the definition of ``species'' to insert,
``A distinct population segment `interbreeds when mature' when it
consists of members of the same species or subspecies in the wild that
are capable of interbreeding when mature.'' We have removed the
proposed language from the definition of ``species'' in this final rule
and left only the language in the preamble. The Services are not
amending the definition.
(58) Comment: A commenter suggested that the Services clarify the
meaning of ``being considered by the Secretary'' in the definition of
the term ``candidate.'' The commenter suggested that the final rule
substitute the more narrow definition found in the FWS candidate
species fact sheet, which states: ``Candidate species are plants and
animals for which the U.S. Fish and Wildlife Service has sufficient
information on their biological status and threats to propose them as
endangered or threatened under the Endangered Species Act, but for
which development of a proposed listing regulation is precluded by
other higher priority listing activities.''
Our Response: We agree with the commenter that the statement in the
FWS candidate fact sheet is an appropriate meaning of the phrase
``being considered by the Secretary'' found in the definition of
candidate. We emphasize that we did not change the definition of
``candidate'' in this regulation.
Criteria for Designating Critical Habitat
(59) Comment: The Western Governors' Association requested that the
Services provide a thorough, data-based explanation of the basis for
the determination that areas outside the range occupied at the time of
listing are or will be essential habitat.
[[Page 7425]]
Our Response: Under section 3(5)(A)(ii) of the Act, to designate as
critical habitat specific areas that are outside the geographical area
occupied by the species at the time the species is listed, the Services
must determine that the areas are essential for the conservation of the
species. This determination must be based on the best scientific data
available concerning the particular species and its conservation needs.
When the Services propose to designate specific areas pursuant to
section 3(5)(A)(ii), they have under the existing regulations and will
under the revised regulations explain the basis for the determination,
including the supporting data. Thus, the Services' explanation will be
available for public comment.
(60) Comment: Several commenters, including one State, were
concerned that the essential areas in unoccupied areas may not even be
suitable for the species and that this is an erroneous and unreasonable
interpretation of an otherwise clear statutory statement and should be
withdrawn.
Our Response: Section 3(5)(A)(ii) of the Act expressly allows for
the consideration and inclusion of unoccupied habitat in a critical
habitat designation if such habitat is determined to be essential for
the conservation of the subject species. These areas do not have to
contain the physical or biological features and are not subject to a
finding that they may require special management considerations or
protection. This is in contrast to what is required under the first
part of the definition of ``critical habitat'' (section 3(5)(A)(i) of
the Act) for areas occupied at the time of listing.
(61) Comment: Several commenters stated that the Services may only
properly make a ``not prudent'' finding if there is specific
information that increased poaching would result from designating
critical habitat.
Our Response: We respectfully disagree with the commenters'
assertion. The current regulations (49 FR 38900; October 1, 1984, and
at 50 CFR 424.12(a)(1)) allow for a determination that critical habitat
is not prudent for a species if such designation would: (1) Increase
the degree of threat to the species through the identification of
critical habitat, or (2) not be beneficial to the species. The
determination that critical habitat is not prudent for a listed species
is uncommon, especially given that most species are listed, in part,
because of impacts to their habitat or curtailment of their range. Most
``not prudent'' findings have resulted from a determination that there
would be increased harm or threats to a species through the
identification of critical habitat. For example, if a species was
highly prized for collection or trade, then identifying specific
localities of the species could render it more vulnerable to collection
and, therefore, further threaten it. However, in some circumstances, a
species may be listed because of factors other than threats to its
habitat or range, such as disease, and the species may be a habitat
generalist. In such a case, on the basis of the existing and revised
regulations, it is permissible to determine that critical habitat is
not beneficial and, therefore, not prudent. It is also permissible to
determine that a designation would not be beneficial if no areas meet
the definition of ``critical habitat.''
(62) Comment: Several commenters inquired about whether the
Services would revise the regulations to provide greater flexibility in
defining a greater breadth of circumstances where a determination can
be made that the designation of critical habitat for a species is not
beneficial to its conservation and, therefore, not prudent.
Our Response: As noted above, it is permissible under the current
and revised regulations to determine that designating critical habitat
for a species is not beneficial and, therefore, not prudent. The text
of these revised regulations further clarifies the non-exclusive list
of factors the Services may consider in evaluating whether designating
critical habitat is not beneficial. The inclusion of ``but not limited
to'' to modify the statement ``the factors the Services may consider
include'' allows for the consideration of alternative fact patterns
where a determination that critical habitat is not beneficial would be
appropriate. We think it is important to expressly reflect this
regulatory flexibility in the revised regulations. Nonetheless, based
on the Services' history of implementing critical habitat, we
anticipate that making a not-prudent determination on any fact pattern
will be rare.
(63) Comment: One State commented that the Services dropped the
word ``probable'' from the revised Sec. 424.12(a) when talking about
economic impacts and that the word should be retained in the final
rule.
Our Response: We agree and have retained the word ``probable'' in
this final rule. It is consistent with the revised final regulation in
50 CFR 424.19 (78 FR 53058) and our draft policy on exclusions under
section 4(b)(2) of the Act. We note that in this context the term
``probable'' means reasonably likely to occur.
(64) Comment: Several commenters recommended adding after the word
``threat'' in the second sentence to Sec. 424.12(a)(1)(ii), the words
``sufficient to warrant listing the species as threatened or
endangered.''
Our Response: While we agree with the commenters' intent, we find
that adding the phrase would be redundant because we would only be
making a determination as to whether critical habitat is prudent if the
species was either being proposed for listing simultaneously or is
already listed.
(65) Comment: Several commenters thought the Services should simply
delete Sec. 424.12(a)(1)(ii) instead of expanding it. They further
stated that the Act does not require that a species currently be
threatened by habitat loss before critical habitat is designated and
protected, and the spirit of the Act would not be served by the
imposition of such a requirement by regulation.
Our Response: Critical habitat is a conservation tool under the Act
that can provide for the regulatory protection of a species' habitat.
The current regulations and the proposed revisions do not establish a
requirement that a species be threatened by the modification,
fragmentation, or curtailment of its range for critical habitat to be
beneficial and, therefore, prudent to designate. However, the
regulation and revisions establish a framework whereby if a species is
listed under the Act and it is determined through that process that its
habitat is not limited or threatened by destruction, modification, or
fragmentation, then it may not be beneficial or prudent to designate
critical habitat. While this provision is intended to reduce the burden
of regulation in rare circumstances in which designating critical
habitat does not contribute to conserving the species, the Services
recognize the value of critical habitat as a conservation tool and
expect to designate it in most cases.
(66) Comment: Several commenters stated that Sec. 424.12(a)(2) is
not consistent with the plain meaning of the Act and should be deleted
from the final rule. They stated the proposed minor word changes did
not improve the situation.
Our Response: The minor word changes to Sec. 424.12(a)(2) are
meant to make the language more consistent with the language in the
Act. This section is necessary to inform the public as to the
circumstances in which the Services will make a not-determinable
finding on critical habitat and thereby invoking the 1-year extension
of section 4(b)(6)(C)(ii) of the Act. 16 U.S.C. 1533(b)(6)(C)(ii).
[[Page 7426]]
(67) Comment: A commenter stated that when the Services deem
critical habitat as not determinable due to a lack of data for habitat
analyses or lack of knowledge on biological needs of the species, the
Services should regularly check for new data and/or make efforts to
collect necessary data and move forward with critical habitat
designations. One State also commented that critical habitat
designations should only be made based on the best available scientific
data and information, and in instances where data or information is
lacking, the Services have an obligation to delay a designation until
such time that sufficient information is acquired.
Our Response: Finding that critical habitat is not determinable
only invokes a 1-year extension of the deadline for finalizing a
critical habitat designation under section 4(b)(6)(C)(ii) of the Act.
16 U.S.C. 1533(b)(6)(C)(ii). At the conclusion of the year, the
Services must move forward with the designation and have no authority
under the Act to further delay designation (unless we determine that
designation is not prudent). We agree that critical habitat
designations must only be made based on the best scientific data
available as required by the Act. If we initially do not have enough
data to make a critical habitat determination, then we can invoke the
1-year extension allowed under the Act. The Services use that time to
gather additional data. At the end of the 1-year extension, the
Services must use the best scientific data available to make the
critical habitat determination.
(68) Comment: One State suggested that climate change is more
appropriately addressed during a 5-year status review and the critical
habitat revision process than trying to attempt to accommodate future
critical habitat by predicting areas necessary to support the species'
recovery. It further asserted that the Services' proposed authority to
designate areas that are currently unoccupied and which are not now
necessary to support the species' recovery, but may eventually become
necessary, is a vast expansion of the critical habitat program and
contrary to the focus in the Act on current habitat conditions.
Our Response: We agree that 5-year status reviews and the critical
habitat revision process can play important roles regarding the
conservation needs of a species in response to habitat changes
resulting from climate change. However, the statute as written allows
for sufficient flexibility to address the effects of climate change in
a critical habitat designation, and, therefore, the clarifications
provided in our proposal and this final rule do not expand the
Services' authority. There have been specific circumstances, as
discussed in our proposal, where data have been available showing the
shift in habitat use by a species in response to the effects of climate
change. In those cases where the best scientific data available
indicate that a species may be shifting habitats or habitat use, then
it is permissible to include specific areas accommodating these changes
in a designation, provided that the Services can explain why the areas
meet the definition of ``critical habitat.'' Although some such
instances are based on reasonable predictions of how habitat will be
used by the species in the future, they are based on determinations
that the areas are currently essential to the species. In other words,
we may find that an unoccupied area is currently ``essential for the
conservation'' even though the functions the habitat is expected to
provide may not be used by the species until a point in the foreseeable
future. The data and rationale on which such a designation is based
will be clearly articulated in our proposed rule designating critical
habitat. The Services will consider whether habitat is occupied or
unoccupied when determining whether to designate it as critical habitat
and use the best available scientific data on a case-by-case basis
regarding the current and future suitability of such habitat for
recovery of the species, and when developing conservation measures.
(69) Comment: Several commenters requested clarification of new
Sec. 424.12(e) with regard to the differences in the way the Services
handle designation of critical habitat for species listed prior to the
1982 amendments to the Act versus species listed after the 1982
amendments.
Our Response: If the Services designate critical habitat for
species listed prior to the 1982 amendments, the designation is
procedurally treated like a revision of existing critical habitat even
if critical habitat was never designated. Thus, the Services have
additional options at the final rule stage with regard to a proposal to
designate critical habitat for those species listed prior to 1982 that
they do not have when proposing to designate habitat for other species.
These include an option to make a finding that the revision ``should
not be made'' and to extend the 12-month deadline by an additional
period of up to 6 months if there is substantial disagreement regarding
the sufficiency or accuracy of available data (see 16 U.S.C.
1533(b)(6)(B)(i)).
(70) Comment: Several commenters, including two States, indicated
that removing references to ``primary constituent elements''
dramatically and unnecessarily expands the scope of critical habitat
and confuses instead of clarifies critical habitat designation, leading
to more litigation.
Our Response: Removing references to ``primary constituent
elements'' from the regulation will not result in expansion of the
scope of critical habitat. Removing this phrase is not intended to
substantively alter anything about the designation of critical habitat,
but to eliminate redundancy in how we describe the physical or
biological features. The phrase ``primary constituent element'' is not
found in the Act and the regulations have never been clear as to how
primary constituent elements relate to or are distinct from physical or
biological features essential to the conservation of the species, which
is the phrase used in the Act. In fact, the removal of the phrase
``primary constituent elements'' will alleviate the tension caused by
trying to understand the relationship between the phrases. The
specificity of the primary constituent elements that has been discussed
in previous designations will now be discussed in the descriptions of
the physical or biological features essential to the conservation of
the species.
(71) Comment: Several commenters including several States were
opposed to elimination of Sec. 424.12(e) as this section is necessary
and intentionally limiting and is an accurate implementation of the
statutory definition and Congressional intent. Several commenters also
questioned that when the Services promulgated Sec. 424.12(e) in 1980,
that we explained in the preamble to that rule that the limitation in
Sec. 424.12(e) was intended to ``implement the statutory requirement''
that unoccupied areas may be designated ``only if necessary to ensure
the conservation of the species.'' The Services do not address this
prior interpretation at all, or explain why a rule that it once enacted
as necessary to implement a statutory requirement is now unnecessary.
Our Response: We respectfully disagree. Section 424.12(e) did not
allow us to designate unoccupied areas unless a designation limited to
its present range (occupied) would be inadequate to ensure the
conservation of the species. As we stated in the proposed rule, there
is no suggestion in the legislative history that the Services were
expected to exhaust occupied habitat before considering whether any
unoccupied areas may be essential.
[[Page 7427]]
Further, section 3(5)(A) of the Act expressly allows for the
consideration and inclusion of unoccupied habitat in a critical habitat
designation if such habitat is determined to be essential for the
conservation of the subject species. There is no specific language in
the Act that requires the Services to first prove that the inclusion of
all occupied areas in a designation are insufficient to conserve the
species before considering unoccupied areas. However, the existing
implementing regulations state that such unoccupied habitat could only
be considered if a determination was made that the Service(s) could not
recover the species with the inclusion of only the occupied habitat.
We have learned from years of implementing the critical habitat
provisions of the Act that often a rigid step-wise approach, i.e.,
first designating all occupied areas that meet the definition of
``critical habitat'' (assuming that no unoccupied habitat is
designated) and then, only if that is not enough, designating essential
unoccupied habitat, does not necessarily serve the best conservation
strategy for the species and in some circumstances may result in a
designation that is geographically larger, but less effective as a
conservation tool. Our proposed change will allow us to consider the
inclusion of occupied and unoccupied areas in a critical habitat
designation following at minimum a general conservation strategy for
the species. In some cases, we have and may continue to find, that the
inclusion of all occupied habitat in a designation does not support the
best conservation strategy for a species. We expect that the concurrent
evaluation of occupied and unoccupied areas for a critical habitat
designation will allow us to develop more precise and deliberate
designations that can serve as more effective conservation tools.
Additionally, there is no specific language in the Act that requires
the Services to first prove that the inclusion of all occupied areas in
a designation are insufficient to conserve the species before
considering unoccupied areas. The statutory language is sufficiently
clear that it does not need explanation in the revised regulation, and,
moreover, to the extent that the 1980 regulation language differs from
the statutory language, it does not add any clarity.
(72) Comment: Several commenters, including one State, disagreed
that unoccupied areas need not have the features essential to the
conservation of the species and that the Services propose to unlawfully
write this statutory requirement out of the Act. The State also pointed
out that the Services' current position on this issue is distinctly
contrary to the position the Services took in 1984 when the existing
regulations were adopted.
Our Response: Under the second part of the definition of ``critical
habitat'' in the Act (section 3(5)(A)(ii)), the Services are to
identify specific areas outside the geographical area occupied by the
species, at the time it is listed in accordance with the provisions of
section 4 of the Act, upon a determination by the Secretary that such
areas are essential for the conservation of the species. In contrast to
section 3(5)(A)(i), this provision does not mention physical or
biological features, much less require that the specific areas contain
the physical or biological features essential to the conservation of
the species. These are two clearly distinct provisions. The unoccupied
areas do not have to presently contain any of the physical or
biological features, which is not a change from the way we have been
designating unoccupied critical habitat (see, e.g., Markle Interests v.
USFWS, 40 F. Supp. 3d 744 (E.D. La. 2014)).
(73) Comment: One State recommended that the Services develop a
policy or metric to determine whether a particular area should be
designated as critical habitat in unoccupied areas.
Our Response: This final rule explains the Services' general
parameters for designating critical habitat. The details of why a
specific area is determined to be essential to the conservation of the
species will in part be directed by any generalized conservation
strategy developed for the species, and clearly articulated in our
proposed and final rules designating critical habitat. That
determination is a fact-specific analysis and is based on the best
available scientific data for the species and its conservation needs.
The proposed rule for each critical habitat designation will be subject
to public review and comment.
(74) Comment: A commenter suggested that the Services designate
enough critical habitat at the time of listing to ensure that a species
can recover.
Our Response: In evaluating which areas qualify as critical habitat
and specific areas finalized (subject to section 4(b)(2) exclusions,
see final policy published elsewhere in today's Federal Register), we
follow the statutory requirements to identify those occupied areas that
contain the physical or biological features essential to the species'
conservation that may require special management considerations or
protection and any unoccupied areas that we determine to be essential
for the species' conservation. Designation of critical habitat is one
important tool that contributes to recovery, but a critical habitat
designation alone may not be sufficient to achieve recovery. Indeed,
given the limited regulatory role of a critical habitat designation
(i.e., through section 7's mandate that Federal agencies avoid
destruction or adverse modification of critical habitat, see final rule
published elsewhere in today's Federal Register), it is generally not
possible to look to a critical habitat designation alone to ensure
recovery. Also, we must designate critical habitat according to
mandatory timeframes, very often prior to development of a formal
recovery plan. See Home Builders Ass'n of Northern Cal. v. U.S. Fish
and Wildlife Service, 616 F.3d 983, 989-90 (9th Cir. 2010). However,
although a critical habitat designation will not necessarily ensure
recovery, it will further recovery because the Services base the
designation on the best available scientific information about the
species' habitat needs at the time of designation. The best available
information will include any generalized conservation strategy or
criteria that may have been developed for the species in consultation
with staff working in recovery planning and implementation to ensure
collaboration, consistency, and efficiency as the Services work with
the public and partners to recover a listed species.
(75) Comment: A commenter stated that the proposed rule clarifies
that the Services have the discretion to designate critical habitat for
species listed before 1978, but does not specify when that discretion
would be used. The commenter requested that the Services identify
guidelines or standards for judging when to designate critical habitat
for pre-1978 species.
Our Response: Whether to exercise discretion to designate critical
habitat for species listed prior to 1978 is a case-specific
determination dependent on the conservation needs of the species,
scientific data available, and the resources available for additional
rulemaking. Guidelines on this point could limit Secretarial discretion
and may not allow for sufficient flexibility in furthering the
conservation of a species.
(76) Comment: Several commenters were concerned that the Services
must commit to using the best scientific data available when
designating unoccupied areas as critical habitat.
Our Response: We are mandated by the Act to use (and are committed
to using) the best scientific data available in determining any
specific areas as critical habitat, regardless of occupancy.
[[Page 7428]]
(77) Comment: Several Tribes stated that while the Services readily
acknowledge in the proposal their responsibility to communicate
meaningfully with recognized Federal Tribes on a government-to-
government basis, the proposed revision does nothing to clarify how the
Services will carry out this responsibility.
Our Response: These revised regulations set forth our general
practice for designating critical habitat, clarify definitions and
phrases, and in general align the regulations with the statute. The
revised regulations are not intended to be prescriptive in how the
Services will implement the provisions or coordinate with federally
recognized Tribes that are potentially affected. However, the Services
are committed to communicate and coordinate meaningfully and
effectively with federally recognized Tribes concerning actions under
the ESA, including the development and implementation of critical
habitat for species that may occur on their lands. We rely on the
requirements of S.O. 3206 to provide the guidance on how the Services
will carry out this responsibility. We have often found that the best
and most meaningful coordination and collaboration, including
fulfilling our responsibilities under S.O. 3206, occurs between our
Regional and field offices and a specific Tribe on a particular
species.
(78) Comment: Several commenters were opposed to the inclusion of
the proposed Sec. 424.12(g), saying the Act makes no distinction
between foreign and domestic species and requires that all listed
species receive critical habitat unless doing so is not prudent or
determinable.
Our Response: We respectfully disagree. Subsection (g) is a
continuation of existing subsection (h), which has long codified the
Services' understanding that critical habitat should not be designated
outside of areas under United States jurisdiction. This interpretation
is well supported. The Act makes a distinction between coordination
with and implementation of the provisions of the ESA between States and
local jurisdictions within the United States versus with foreign
countries. Section 4(b)(1)(A), which deals with listing species,
provides that the Secretary shall consult, as appropriate, not only
with affected States, but also, in cooperation with the Secretary of
State, with the country or countries in which the species is normally
found. In contrast, section 7 of the ESA does not include a requirement
to consult with foreign governments. Further, section 8(b)(1) states
that ``the Secretary, through the Secretary of State, shall encourage--
(1) foreign countries to provide for the conservation of fish or
wildlife and plants including endangered species and threatened species
listed pursuant to section 4.'' It is clear that Congress understood
the distinction between implementing the ESA within the jurisdiction of
the United States and implementing the ESA within the jurisdiction of
foreign countries. It then follows that since Congress did not
explicitly state that critical habitat shall be designated in foreign
countries or that the Secretary consult, as appropriate, with foreign
countries on a designation of critical habitat, then the designation of
critical habitat is limited to lands within the jurisdiction of the
United States.
Justice Stevens approved of the Services' conclusion in his
concurrence in Lujan v. Defenders of Wildlife, 504 U.S. 555 (1992).
There, he favorably noted the Service's longstanding interpretation of
the limitation of critical habitat designations to areas within the
jurisdiction of the United States:
The Secretary of the Interior and the Secretary of Commerce have
consistently taken the position that they need not designate
critical habitat in foreign countries. See 42 FR 4869 (1977)
(initial regulations of the Fish and Wildlife Service and the
National Marine Fisheries Service on behalf of the Secretary of the
Interior and the Secretary of Commerce). Consequently, neither
Secretary interprets Sec. 7(a)(2) to require federal agencies to
engage in consultations to ensure that their actions in foreign
countries will not adversely affect the critical habitat of
endangered or threatened species.
That interpretation is sound. . . .
Id. at 587 (Stevens, J., concurring).
(79) Comment: One State requested that the Services include a new
Sec. 424.12(e) that requires that designation will be made after
consultation with the affected States. It would read, ``In designating
any area as critical habitat, the Secretary shall consult with affected
States (those in which the proposed critical habitat is located or
those that may be affected by the designation of the habitat) prior to
completing the designation, and the fact of and finding of such
consultation shall be addressed in the final rulemaking for the
designation.''
Our Response: The suggested new Sec. 424.12(e) is not necessary
because section 4(b)(5)(A)(ii) of the Act requires the Secretary to
give actual notice of the proposed regulation (including the complete
text of the regulation) to the State agency in each State in which the
species is believed to occur, and to each county or equivalent
jurisdiction in which the species is believed to occur, and invite the
comment of such agency, and each such jurisdiction. Further, section
4(i) of the Act requires the Secretary to provide a written
justification for adopting regulations in conflict with the agency's
comments or for failing to adopt a regulation as requested in a State
petition. In addition to these requirements, the Services are committed
to continuing to work with the States early in the process to ensure
that we are using the best scientific data available.
(80) Comment: One State requested clarification on the application
of this regulation to critical habitat designations that are currently
under way, but not yet finalized.
Our Response: As indicated in DATES above, although effective 30
days from the date of publication, the revised version of Sec. 424.12
will apply only to rulemakings for which the proposed rule is published
after that date. Thus, the prior version of Sec. 424.12 will continue
to apply to any rulemakings for which a proposed rule was published
before that date. However, because many of the revisions merely codify
or explain our existing practices and interpretations, we may
immediately refer to and act consistent with the amended language of
Sec. 424.12 in final rules to which the prior version applies.
(81) Comment: Several commenters objected to the Services'
determination that a regulatory flexibility analysis is not required
for this regulation, stating the regulated community is affected by
this regulation.
Our Response: We respectfully disagree. We interpret the Regulatory
Flexibility Act, as amended, to require that Federal agencies evaluate
the potential incremental impacts of rulemaking only on those entities
directly regulated by the rulemaking itself and, therefore, not on
indirectly regulated entities. Recent case law supports this
interpretation (https://www.sba.gov/sites/default/files/rfaguide_0512_0.pdf, pages 22-23). NMFS and FWS are the only entities
that are directly affected by this rule because we are the only
entities that designate critical habitat, and this rule pertains to the
procedures for carrying out those designations. No external entities,
including any small businesses, small organizations, or small
governments, will experience any direct economic impacts from this
rule.
We understand that there is considerable confusion as to how these
revisions to the regulation will change the process for designating
critical
[[Page 7429]]
habitat, with many thinking it will greatly expand our designations and
provide less clarity to the process. We went to great effort in our
proposal and further in this final rule to explain that revised
regulations will not result in any significant deviation from how the
two agencies have been designating critical habitat. Our intent is to
codify what we have been doing for many years and provide common-sense
revisions based on lessons learned and relevant case law. It is our
expectation that these revisions will allow us to develop more precise
and deliberate designations that can serve as more effective
conservation tools, focusing conservation resources where needed and
minimizing regulatory burdens where not necessary. As a consequence, we
find, as iterated above, that NMFS and FWS are the only entities
directly regulated by these revisions and that an RFA analysis is not
required.
(82) Comment: We received several comments that the proposed
revised regulations constituted a major Federal action because they
will result in significant socioeconomic consequences and these impacts
must be analyzed under the National Environmental Policy Act of 1969
(NEPA).
Our Response: As detailed in the REQUIRED DETERMINATIONS section
below, we have determined that this action qualifies for a categorical
exclusion under both DOI and NOAA governing procedures.
Final Amendments to Regulations Discussion of Changes to Part 424
This final rule revises 50 CFR 424.01, 424.02, and 424.12 (except
for paragraph (c)) to clarify the procedures and criteria used for
designating critical habitat, addressing in particular several key
issues that have been subject to frequent litigation.
In finalizing the specific changes to the regulations that follow,
and setting out the accompanying clarifying discussion in this
preamble, the Services are establishing prospective standards only. As
indicated in DATES above, although effective 30 days from the date of
publication, the revised version of Sec. 424.12 will apply only to
rulemakings for which the proposed rule is published after that date.
Thus, the prior version of Sec. 424.12 will continue to apply to any
rulemakings for which a proposed rule was published before that date.
However, because many of the revisions merely codify or explain our
existing practices and interpretations, we may immediately refer to and
act consistent with the amended language of Sec. 424.12 in final rules
to which the prior version applies. Nothing in these final revised
regulations is intended to require that any previously completed
critical habitat designation must be reevaluated on this basis.
Section 424.01 Scope and Purpose
We are making minor revisions to this section to update language
and terminology. The first sentence in Sec. 424.01(a) is being revised
to remove reference to critical habitat being designated or revised
only ``where appropriate.'' This wording implied a greater flexibility
regarding whether to designate critical habitat than is correct.
Circumstances in which we determine critical habitat designation is not
prudent are rare. Therefore, the new language removes the phrase
``where appropriate.'' Other revisions to this section are minor word
changes to use more plain language or track the statutory language.
Section 424.02 Definitions
This section of the regulations defines terms used in the context
of section 4 of the Act. We are making revisions to Sec. 424.02 to
update it to current formatting guidelines, to revise several
definitions related to critical habitat, to delete definitions that are
redundant with statutory definitions, and to add two newly defined
terms. Section 424.02 is currently organized with letters as paragraph
designation for each term (e.g., Sec. 424.02(b) Candidate). The Office
of the Federal Register now recommends setting out definitions in the
CFR without paragraph designations. We propose to revise the formatting
of the entire section accordingly. Discussion of the revised
definitions and newly defined terms follows. We note where these final
revisions differ from those set out in the proposed rule.
We note that, although revising the formatting of the section
requires that the entirety of the section be restated in the final-
amended-regulation section, we are not at this time revisiting the text
of those existing definitions that we are not specifically revising,
including those that do not directly relate to designating critical
habitat. In particular, we are not in this rulemaking amending the
definitions of ``plant,'' ``wildlife,'' or ``fish and wildlife'' to
reflect changes in taxonomy since the ESA was enacted in 1973. In 1973,
only the Animal and Plant Kingdoms of life were universally recognized
by science, and all living things were considered to be members of one
of these kingdoms. Thus, at enactment, the ESA applied to all living
things. Advances in taxonomy have subsequently split additional
kingdoms from these two. Any species that was considered to be a member
of the Animal or Plant Kingdoms in 1973 will continue to be treated as
such for purposes of the administration of the Act regardless of any
subsequent changes in taxonomy. We may address this issue in a future
rulemaking relating to making listing determinations (as opposed to
designating critical habitat). In the meantime, the republication of
these definitions here should not be viewed as an agency determination
that these definitions reflect the scope of the Act in light of our
current understanding of taxonomy.
The current regulations include a definition for ``Conservation,
conserve, and conserving.'' We are revising the title of this entry to
``Conserve, conserving, and conservation,'' changing the order of the
words to conform to the statute. Additionally, we are revising the
first sentence of the definition to include the phrase ``i.e., the
species is recovered'' to clarify the link between conservation and
recovery of the species. The statutory definition of ``conserve,
conserving, and conservation'' is ``to use and the use of all methods
and procedures that are necessary to bring any endangered or threatened
species to the point at which measures provided pursuant to the Act are
no longer necessary.'' This is the same concept as the definition of
``recovery'' found in Sec. 402.02: ``improvement in the status of
listed species to the point at which listing is no longer
appropriate.'' The Services, therefore, view ``conserve, conserving,
and conservation'' as a process culminating at the point at which a
species is recovered.
We are deleting definitions for ``critical habitat,'' ``endangered
species,'' ``plant,'' ``Secretary,'' ``State Agency,'' and ``threatened
species'' because these terms are defined in the Act and the existing
regulatory definitions do not add meaning to the terms.
We also define the previously undefined term ``geographical area
occupied by the species'' as: ``the geographical area which may
generally be delineated around the species' occurrences, as determined
by the Secretary (i.e., range). Such areas may include those areas used
throughout all or part of the species' life cycle, even if not used on
a regular basis (e.g., migratory corridors, seasonal habitats, and
habitats used periodically, but not solely by vagrant individuals).''
This term appears in the definition of ``critical habitat'' found in
section 3(5)(A)(i) and (ii) of the Act, but is not defined in the Act
or in our current regulations. The inclusion of this new
[[Page 7430]]
regulatory definition reflects the Services' efforts to clarify the
critical-habitat-designation process.
The definition of ``critical habitat'' in the Act has two parts,
section 3(5)(A)(i) and (ii), which establish two distinct categories of
critical habitat, based on species occupancy in an area at the time of
listing. Therefore, to identify specific areas to designate as critical
habitat, we must first determine what area constitutes the
``geographical area occupied by the species at the time of listing,''
which is the language used in the Act. The scale of this area is likely
to be larger than the specific areas that would then be analyzed for
potential designation under section 3(5)(A)(i). This is because the
first part of the critical habitat definition in the Act directs the
Services to identify ``specific areas within'' the geographical area
occupied by the species at time of listing. This intentional choice to
use more narrow terminology alongside broader terminology suggests that
the ``geographical area'' was expected most often to be a larger area
that could encompass multiple ``specific areas.'' Thus, we find the
statutory language supports the interpretation of equating the
geographical area occupied by the species to the wider area around the
species' occurrences at the time of listing. A species' occurrence is a
particular location in which members of the species are found
throughout all or part of their life cycle. The geographic area
occupied by the species is thus the broader, coarser-scale area that
encompasses the occurrences, and is what is often referred to as the
``range'' of the species.
In the Act, the term ``geographical area occupied by the species''
is further modified by the clause ``at the time it is listed.''
However, if critical habitat is being designated or revised several
years after the species was listed, it can be difficult to discern what
was occupied at the time of listing. The known distribution of a
species can change after listing for many reasons, such as discovery of
additional localities, extirpation of populations, or emigration of
individuals to new areas. In many cases, information concerning a
species' distribution, particularly on private lands, is limited as
surveys are not routinely carried out on private lands unless performed
as part of an environmental analysis for a particular development
proposal. Even then, such surveys typically focus on listed rather than
unlisted species, so our knowledge of a species' distribution at the
time of listing in these areas is often limited and the information in
our listing rule may not detail all areas occupied by the species at
that time.
Thus, while some of these changes in a species' known distribution
reflect changes in the actual distribution of the species, some reflect
only changes in the quality of our information concerning distribution.
In these circumstances, the determination of which geographic areas
were occupied at the time of listing may include data developed since
the species was listed. This interpretation was supported by a recent
court decision, Otay Mesa Property L.P. v. DOI, 714 F. Supp. 2d 73
(D.D.C. 2010), rev'd on other grounds, 646 F.3d 914 (D.C. Cir. 2011)
(San Diego fairy shrimp). In that decision, the judge noted that the
clause ``occupied at the time of listing'' allows FWS to make a post-
listing determination of occupancy based on the currently known
distribution of the species in some circumstances. Although the D.C.
Circuit disagreed with the district court that the record contained
sufficient data to support the FWS' determination of occupancy in that
case, the D.C. Circuit did not express disagreement with (or otherwise
address) the district court's underlying conclusion that the Act allows
FWS to make a post-listing determination of occupancy if based on
adequate data. The FWS acknowledges that to make a post-listing
determination of occupancy we must distinguish between actual changes
to species occupancy and changes in available information. For
succinctness, herein and elsewhere we refer to areas as ``occupied''
when we mean ``occupied at the time of listing.''
The second sentence of the definition for ``geographical area
occupied by the species'' clarifies that the meaning of the term
``occupied'' includes specific areas that are used only periodically or
temporarily by a listed species during some portion of its life
history, and is not limited to those areas where the listed species may
be found more or less continuously. Areas of periodic use may include,
for example, breeding areas, foraging areas, and migratory corridors.
The Ninth Circuit recently supported this interpretation by FWS,
holding that a determination that a species was likely to be
temporarily present in the areas designated as critical habitat was a
sufficient basis for determining those areas to be occupied, even if
the species was not continuously present. Arizona Cattle Growers'
Assoc. v. Salazar, 606 F.3d 1160 (9th Cir. 2010) (Mexican spotted owl).
Nonetheless, periodic use of an area does not include use of
habitat in that area by vagrant individuals of the species who wander
far from the known range of the species. Occupancy by the listed
species must be based on evidence of regular periodic use by the listed
species during some portion of the listed species' life history.
However, because some species are difficult to survey or we may
otherwise have incomplete survey information, the Services will rely on
the best available scientific data, which may in some cases include
indirect or circumstantial evidence, to determine occupancy. We further
note that occupancy does not depend on identifiable presence of adult
organisms. For example, periodical cicadas occupy their range even
though adults are only present for 1 month every 13 or 17 years.
Similarly, the presence (or reasonably determined presence) of eggs or
cysts of fairy shrimp or seed banks of plants constitute occupancy even
when mature individuals are not present.
We also finalize a definition for the term ``physical or biological
features.'' This phrase is used in the statutory definition of
``critical habitat'' to assist in identifying the specific areas within
the entire geographical area occupied by the species that can be
considered for designation as critical habitat. We define ``physical or
biological features'' as ``the features that support the life-history
needs of the species, including but not limited to water
characteristics, soil type, geological features, sites, prey,
vegetation, symbiotic species, or other features. A feature may be a
single habitat characteristic, or a more complex combination of habitat
characteristics. Features may include habitat characteristics that
support ephemeral or dynamic habitat conditions. Features may also be
expressed in terms relating to principles of conservation biology, such
as patch size, distribution distances, and connectivity.''
The definition clarifies that physical and biological features can
be the features that support the occurrence of ephemeral or dynamic
habitat conditions. For example, a species may require early-
successional riparian vegetation in the Southwest to breed or feed.
Such vegetation may exist only 5 to 15 years after a local flooding
event. The necessary features, then, may include not only the suitable
vegetation itself, but also the flooding events, topography, soil type,
and flow regime, or a combination of these characteristics and the
necessary amount of the characteristics that can result in the periodic
occurrence of the suitable vegetation. Thus, the Services could
conclude that essential physical or biological features exist in a
specific area even in the temporary absence of
[[Page 7431]]
suitable vegetation, and could designate such an area as critical
habitat if all of the other applicable requirements were met and if
there were documented occurrences of the particular habitat type in the
area and a reasonable expectation of that habitat occurring again.
In Cape Hatteras Access Preservation Alliance v. DOI, 344 F. Supp.
2d 108, 123 n.4 (D.D.C. 2004), the court rejected FWS' designation for
the piping plover as including lands that did not currently contain the
features defined by FWS, but noted that it was not addressing ``whether
dynamic land capable of supporting plover habitat can itself be one of
the `physical or biological features' essential to conservation.'' The
new definition for ``physical or biological features'' clarifies that
features can be dynamic or ephemeral habitat characteristics. However,
an area within the geographical area occupied by the species,
containing habitat that is not ephemeral by nature but that has been
degraded in some way, must have one or more of the physical or
biological features at the time of designation.
Having defined ``physical or biological features,'' we are also
removing the term ``primary constituent element'' and all references to
it from the regulations in Sec. 424.12. As with all other aspects of
these revisions, this will apply only to future critical habitat
designations and is further explained below in the discussion of the
changes to Sec. 424.12, where the term is currently used.
We are also revising the definition of ``special management
considerations or protection'' which is found in Sec. 424.02. Here we
remove the phrase ``of the environment'' from the current regulation.
This phrase is not used in this context elsewhere in the regulations or
the Act and, therefore, may create ambiguity. We also insert the words
``essential to'' to conform to the language of the Act.
In determining whether an area has essential features that may
require special management considerations or protection, the Services
do not base their decision on whether management is currently in place
or whether that management is adequate. FWS formerly took the position
that special management considerations or protection was required only
if whatever management was in place was inadequate and that additional
special management was needed. This position was rejected by the court
in Center for Biological Diversity v. Norton, 240 F. Supp. 2d 1090 (D.
Ariz. 2003) (Mexican spotted owl), the only court to address this
issue. The Services agree with the conclusion of the court on this
point--it is incorrect to read the statute as asking whether additional
special management considerations or protection may be required. The
evaluation of whether features in an area may require special
management considerations or protection occurs independent of whether
any form of management or protection occurs in the area.
We expect that, in most circumstances, the physical or biological
features essential to the conservation of endangered species may
require special management in all areas in which they occur,
particularly for species that have significant habitat-based threats.
However, if in some areas the essential features do not require special
management consideration or protection because there are no applicable
threats to the features that have to be managed or protected for the
conservation of the species, then that area does not meet this part
(section 3(5)(A)(i)) of the definition of ``critical habitat.''
Nevertheless, we expect such circumstances to be rare.
Furthermore, it is not necessary that a feature currently requires
special management considerations or protection, only that it may
require special management to meet the definition of ``critical
habitat.'' 16 U.S.C. 1532(5)(A)(i) (emphasis added). Two district court
decisions have emphasized this point. CBD v. Norton (Mexican spotted
owl); Cape Hatteras Access Preservation Alliance v. DOI, 344 F. Supp.
2d 108 (D.D.C. 2004) (piping plover). The legislative history supports
the view that Congress purposely set the standard as ``may require.''
Earlier versions of the bills that led to the statutory definition of
``critical habitat'' used the word ``requires,'' but ``may require''
was substituted prior to final passage. In any case, an interpretation
of a statute should give meaning to each word Congress chose to use,
and our interpretation gives the word ``may'' meaning.
Finally, we explain our interpretation of the meaning of the phrase
`interbreeds when mature,' which is found in the definition of
`species.' The ``interbreeds when mature'' language is ambiguous
(Modesto Irrigation Dist. v. Gutierrez, 619 F.3d 1024, 1032 (9th Cir.
2010)). Although we are not revising the regulatory definition of
``species'' at this time, we are using this notice to inform the public
of our interpretation of this phrase.'' We have always understood the
phrase ``interbreeds when mature'' to mean that a DPS consists of
members of the same species or subspecies that when in the wild would
be biologically capable of interbreeding if given the opportunity, but
all members need not actually interbreed with each other. A DPS is a
subset of a species or subspecies, and cannot consist of members of
different species or subspecies. The ``biological species'' concept,
which defines species according to a group of organisms' actual or
potential ability to interbreed, and their relative reproductive
isolation from other organisms, is one widely accepted approach to
defining species. We interpret the phrase ``interbreeds when mature''
to reflect this understanding and to signify only that a DPS must be
composed solely of members of the same species or subspecies. As long
as this requirement is met, a DPS may include multiple groups of
vertebrate organisms that do not actually interbreed with each other.
For example, a DPS may consist of multiple groups of a fish species
separated into different drainages. While it is possible that the
members of these groups do not actually interbreed with each other,
their members are biologically capable of interbreeding.
Our intent was to explain how we have interpreted the phrase, but
by inadvertently including this interpretation in the regulatory
language of the proposed rule, we in fact were proposing to change the
definition of ``species'' to insert, ``A distinct population segment
`interbreeds when mature' when it consists of members of the same
species or subspecies in the wild that are capable of interbreeding
when mature.'' We have removed the proposed language from the
definition of ``species'' in this final rule and left only the language
in this preamble. We also noticed that we inadvertently left out the
word ``Includes'' from the definition of ``species'' in our proposed
regulation. We have restored the word ``Includes'' in this final
regulation to match the definition of ``species'' found in our 1984
regulation. The Services are not substantively amending the definition
at this time.
Section 424.12 Criteria for Designating Critical Habitat
We are revising the first sentence of paragraph (a) to clarify that
critical habitat shall be proposed and finalized ``to the maximum
extent prudent and determinable . . . concurrent with issuing proposed
and final listing rules, respectively.'' The language of the existing
regulation is ``shall be specified to the maximum extent prudent and
determinable at the time a species is proposed for listing.'' We added
the words ``proposed and finalized'' to be
[[Page 7432]]
consistent with the Act, which requires that critical habitat be
finalized concurrent with listing to the maximum extent prudent and
determinable. The existing language could be interpreted to mean
proposing critical habitat concurrent with listing was the only
requirement. Additionally, the existing phrase ``shall be specified''
is vague and not consistent with the requirement of the Act, which is
to propose and finalize a designation of critical habitat. The last two
sentences in paragraph (a) contain minor language changes to use the
active voice.
Paragraphs (a)(1) and (a)(1)(i) are not changed.
The first sentence of paragraph (a)(1)(ii) remains the same.
However, we add a second sentence to paragraph (a)(1)(ii) to provide
examples of factors that we may consider in determining whether a
designation would not be beneficial to the species. A designation may
not be beneficial and, therefore, not prudent, under certain
circumstances, including but not limited to: Whether the present or
threatened destruction, modification, or curtailment of a species'
habitat or range is not a threat to the species, or whether no areas
meet the definition of ``critical habitat.'' For example, this
provision may apply to a species that is threatened primarily by
disease but the habitat that it relies upon continues to exist
unaltered throughout an appropriate distribution that, absent the
impact of the disease, would support conservation of the species.
Another example is a species that occurs in portions of the United
States and a foreign nation. In the foreign nation, there are multiple
areas that have the features essential to the conservation of the
species; however, in the United States there are no such areas.
Consequently, there are no areas within the United States that meet the
definition of ``critical habitat'' for the species. Therefore, there is
no benefit to designation of critical habitat, and designation is not
prudent.
While this provision is intended to reduce the burden of regulation
in rare circumstances in which designation of critical habitat does not
contribute to the conservation of the species, the Services recognize
the value of critical habitat as a conservation tool and expect to
designate it in most cases.
Section 424.12(a)(2) remains unchanged from the current regulation,
and subparagraphs (i) and (ii) contain minor language changes to be
consistent with the language in the Act.
The Services are completely revising Sec. 424.12(b) of the current
regulations. For the reason explained below, we also remove the terms
``principal biological or physical constituent elements'' and ``primary
constituent elements'' from this section. These concepts are replaced
by the statutory term ``physical or biological features,'' which we
define as described above.
The first part of the statutory definition of ``critical habitat''
(section 3(5)(A)(i)) contains terms necessary for (1) identifying
specific areas within the geographical area occupied by the species
that may be considered for designation as critical habitat and (2)
describing which features on those areas are essential to the
conservation of species. In addition, current Sec. 424.12(b)
introduced the phrase ``primary constituent elements.'' However, the
regulations are not clear as to how primary constituent elements relate
to or are distinct from physical or biological features, which is the
term used in the statute. Adding a term not found in the statute that
is at least in part redundant with the term ``physical or biological
features'' has proven confusing. Trying to parse features into elements
and give them meaning distinct from one another has added an
unnecessary layer of complication and confusion during the designation
process.
The definition of ``physical or biological features,'' described
above, encompasses similar habitat characteristics as currently
described in Sec. 424.12(b), such as roost sites, nesting grounds,
spawning sites, feeding sites, seasonal wetland or dryland, water
quality or quantity, host species or plant pollinator, geological
formation, vegetation type, tide, and specific soil types. Our proposal
is intended to simplify and clarify the process, and to remove
redundancy, without substantially changing the manner in which critical
habitat is designated. The Services still expect to provide a
comparable level of detail and specificity in defining and describing
physical or biological features essential to the conservation of a
species.
Section 424.12(b) describes the process to be used to identify the
specific areas to be considered for designation as critical habitat,
based on the statutory definition of ``critical habitat.'' With respect
to both parts of the definition, the revised regulations emphasize that
the Secretary will identify areas that meet the definition ``at a scale
determined by the Secretary to be appropriate.'' The purpose of this
language is to clarify that the Secretary cannot and need not make
determinations at an infinitely fine scale. Thus, the Secretary need
not determine that each square inch, square yard, acre, or even square
mile independently meets the definition of ``critical habitat.'' Nor
will the Secretary necessarily consider legal property lines in making
a scientific judgment about what areas meet the definition of
``critical habitat.'' Instead, the Secretary has discretion to
determine at what scale to do the analysis. In making this
determination, the Secretary may consider, among other things, the life
history of the species, the scales at which data are available, and
biological or geophysical boundaries (such as watersheds), and any
draft conservation strategy that may have been developed for the
species.
Under the first part of the statutory definition, in identifying
specific areas for consideration, the Secretary must first identify the
geographical area occupied by the species at the time of listing.
Within the geographical area occupied by the species, the Secretary
must identify the specific areas on which are found those physical or
biological features (1) essential to the conservation of the species,
and (2) which may require special management considerations or
protection.
Under Sec. 424.12(b)(1)(i), the Secretary will identify the
geographical area occupied by the species using the new regulatory
definition of this term. Under Sec. 424.12(b)(1)(ii), the Secretary
will then identify those physical and biological features essential to
the conservation of the species. These physical or biological features
are to be described at an appropriate level of specificity, based on
the best scientific data available at the time of designation. For
example, physical features might include gravel of a particular size
required for spawning, alkali soil for germination, protective cover
for migration, or susceptibility to flooding or fire that maintains
early-successional habitat characteristics. Biological features might
include prey species, forage grasses, specific kinds or ages of trees
for roosting or nesting, symbiotic fungi, or a maximum level of
nonnative species consistent with conservation needs of the listed
species. The features may also be combinations of habitat
characteristics and may encompass the relationship between
characteristics or the necessary amount of a characteristic needed to
support the life history of the species. For example, a feature may be
a specific type of forage grass that is in close proximity to a certain
type of shrub for cover. Because the species would not consume the
grass if there were not the nearby shrubs in which to hide from
predators, one of these characteristics in isolation would not be an
essential feature; the feature that supports the life-history needs of
the
[[Page 7433]]
species would consist of the combination of these two characteristics
in close proximity to each other.
In considering whether features are essential to the conservation
of the species, the Services may consider an appropriate quality,
quantity, and spatial and temporal arrangement of habitat
characteristics in the context of the life-history needs, condition,
and status of the species. For example, a small patch of meadow may
have the native flowers, full sun, and a biologically insignificant
level of invasive ants that have been determined to be important
habitat characteristics that support the life-history needs of an
endangered butterfly. However, that small patch may be too far away
from other patches to allow for mixing of the populations, or the
meadow may be too small for the population to persist over time. So the
area could have important characteristics, but those characteristics
may not contribute to the conservation of the species because they lack
the appropriate size and proximity to other meadows with similar
characteristics. Conversely, the exact same characteristics (native
flowers, full sun, and a biologically insignificant level of invasive
ants), when combined with the additional characteristics of larger size
and short dispersal distance to other meadows, may in total constitute
a physical or biological feature essential to the conservation of the
species.
Under Sec. 424.12(b)(1)(iii), the Secretary will then determine
the specific areas within the geographical area occupied by the species
on which are found those physical or biological features essential to
the conservation of the species.
Section 424.12(b)(1)(iv) provides for the consideration of whether
those physical or biological features may require special management
considerations or protection. In this portion of the analysis, the
Secretary must determine whether there are any ``methods or procedures
useful in protecting physical and biological features for the
conservation of listed species.'' Only those physical or biological
features that may be in need of special management considerations or
protection are considered further. The Services may conduct this
analysis for the need of special management considerations or
protection at the scale of all specific areas, but they may also do so
within each specific area.
The ``steps'' outlined in subparagraphs (i) through (iv) above are
not necessarily intended to be applied strictly in a stepwise fashion.
The instructions in each subparagraph must be considered, as each
relates to the statutory definition of ``critical habitat.'' However,
there may be multiple pathways in the consideration of the elements of
the first part of the definition of ``critical habitat.'' For instance,
one may first identify specific areas occupied by the species, then
identify all features needed by a species to carry out life-history
functions in those areas through consideration of the conservation
needs of the species, and then determine which of those specific areas
contain the features essential to the conservation of the species. The
determination of which features are essential to the conservation of
the species may consider the spatial arrangement and quantity of such
features in the context of the life history, status, and conservation
needs of the species. In some circumstances, not every location that
contains one or more of the habitat characteristics that a species
needs will be designated as critical habitat. Some locations may have
important habitat characteristics, but are too small to support a
population of the species, or are located too far away from other
locations to allow for genetic exchange. Considered in context of any
generalized conservation strategy that might be developed for the
species, Sec. 424.12(b)(1)(i) through (iv) will allow for sufficient
flexibility to determine what areas within the geographical area
occupied by the species are needed to provide for the conservation of
the species.
Occasionally, new taxonomic information may result in a
determination that a previously listed species or subspecies is
actually two or more separate entities. In such an instance, the
Services must have flexibility, when warranted, to continue to apply
the protections of the Act to preserve the conservation value of
critical habitat that has been designated for a species listed as one
listable entity (i.e., species, subspecies, or distinct population
segment (DPS)), and which is being reproposed for listing as one or
more different listable entities (e.g., when the Services propose to
list two or more species, subspecies, or DPSs that had previously been
listed as a single entity). Where appropriate (such as where the range
of an entity proposed for listing and a previously designated area of
critical habitat align), the Services have the option to find,
simultaneously with the proposed listing of the proposed entity or
entities, that the relevant geographic area(s) of the existing
designation continues to apply as critical habitat for the new entity
or entities. Such a finding essentially carries forward the existing
critical habitat (in whole or in part). Alternatively, the Services
have the option to pursue a succinct and streamlined notice of proposed
rulemaking to carry forward the existing critical habitat (in whole or
in part), which draws, as appropriate, from the existing designation.
More broadly, when applying Sec. 424.12(b)(1) to the facts
relating to a particular species, the Services will usually have more
than one option available for determining what specific areas
constitute the critical habitat for that species. In keeping with the
conservation-based purpose of critical habitat, the relevant Service
may find it best to first consider broadly what it knows about the
biology and life history of the species, the threats it faces, the
species' status and condition, and, therefore, the likely conservation
needs of the species with respect to habitat. If there already is a
recovery plan for that species (which is not always the case and not a
prerequisite for designating critical habitat), then that plan would be
useful for this analysis.
Using principles of conservation biology such as the need for
appropriate patch size, connectivity of habitat, dispersal ability of
the species, or representation of populations across the range of the
species, the Services may evaluate areas needed for the conservation of
the species. The Services must identify the physical and biological
features essential to the conservation of the species and unoccupied
areas that are essential for the conservation of the species. When
using this methodology to identify areas within the geographical area
occupied by the species at the time of listing, the Services will
expressly translate the application of the relevant principles of
conservation biology into the articulation of the features. Aligning
the physical and biological features identified as essential with the
conservation needs of the species and any conservation strategy that
may have been developed for the species allows us to develop more
precise designations that can serve as more effective conservation
tools, focusing conservation resources where needed and minimizing
regulatory burdens where not necessary.
We note that designation of critical habitat relies on the best
available scientific data at the time of designation. The Services may
not know of, or be able to identify, all of the areas on which are
found the features essential to the conservation of a species. After
designation of final critical habitat for a particular species, the
Services may become aware of or identify other
[[Page 7434]]
features or areas essential to the conservation of the species, such as
through 5-year reviews and recovery planning. Newly identified features
that are useful for characterizing the conservation value of designated
critical habitat can be considered in consultations conducted under
section 7(a)(2) of the Act as part of the best available scientific and
commercial data. We also note that if there is uncertainty as to
whether an area was ``within the geographical area occupied by the
species, at the time it is listed,'' the Services may in the
alternative designate the area under the second part of the definition
if the relevant Service determines that the area is essential for the
conservation of the species.
The second part of the statutory definition of ``critical habitat''
(section 3(5)(A)(ii)) provides that areas outside the geographical area
occupied by the species at the time of listing should be designated as
critical habitat if they are determined to be ``essential for the
conservation of the species.'' Section 424.12(b)(2) further describes
the factors the Services will consider in identifying any areas outside
the geographical area occupied by the species at the time of listing
that may meet this aspect of the definition of ``critical habitat.''
Under Sec. 424.12(b)(2), the Services will determine whether
unoccupied areas are essential for the conservation of the species by
considering ``the life-history, status, and conservation needs of the
species.'' This will be further informed by any generalized
conservation strategy, criteria, or outline that may have been
developed for the species to provide a substantive foundation for
identifying which features and specific areas are essential to the
conservation of the species and, as a result, the development of the
critical habitat designation.
Section 424.12(b)(2) subsumes and supersedes Sec. 424.12(e) of the
existing regulations. Existing section 424.12(e) provides that the
Secretary shall designate areas outside the ``geographical area
presently occupied by a species'' only when ``a designation limited to
its present range would be inadequate to ensure the conservation of the
species.'' Although the existing provision represents one reasonable
approach to giving meaning to the term ``essential'' as it relates to
unoccupied areas, the Services find, based on years of applying the
existing regulations, that this provision is both unnecessary and
unintentionally limiting. While Congress supplied two different
standards to govern the Secretary's designation of these two types of
habitat, there is no suggestion in the legislative history that the
Services were expected to exhaust occupied habitat before considering
whether any unoccupied area may be essential. In addition, although
section 3(5)(C) of the Act reflects Congressional intent that a
designation generally should not include every area that the species
can occupy, this does not necessarily translate into a mandate to avoid
designation of any unoccupied areas unless relying on occupied areas
alone would be insufficient. Indeed, there may be instances in which
particular unoccupied habitat is more important to the conservation of
the species than some occupied habitat.
For example, a species may occupy at low densities a large amount
of habitat that is marginal habitat for the species. That marginal
habitat may nonetheless meet the definition of ``critical habitat''
because the species has been extirpated from what historically was
superior habitat, and it is possible to recover the species if all of
the marginal habitat is thoroughly protected. However, a more certain
and efficient path to recovery may involve the protection of a
relatively small subset of the marginal habitat combined with
protection of some of the superior habitat (allowing for natural
expansion or artificial reintroduction). A variation of this scenario
would involve habitat that may currently be of high quality, but is
unlikely to remain that way due to the effects of climate change. Given
these scenarios, it will be useful for the Services to retain the
flexibility to consider various paths to recovery in considering what
areas to designate as critical habitat.
We conclude that a rigid step-wise approach, i.e., first
designating all occupied areas that meet the definition of ``critical
habitat'' (assuming that no unoccupied habitat is designated) and then,
only if that is not enough, designating essential unoccupied habitat,
does not necessarily serve the best conservation strategy for the
species and, in some circumstances, may result in a designation that is
geographically larger but less effective as a conservation tool.
Deleting current Sec. 424.12(e) will allow us to consider including
occupied and unoccupied areas in a critical habitat designation and to
follow any general conservation strategy, criteria, or outline for the
species that may be developed. We expect that the concurrent evaluation
of occupied and unoccupied areas for a critical habitat designation
will allow us to develop more precise designations that can serve as
more effective conservation tools, focusing conservation resources
where needed and minimizing regulatory burdens where not necessary.
In addition, the existing regulatory provision is unnecessary
because the Secretary in any case must find that the unoccupied area is
``essential.'' In many cases the Secretary may conclude that an
integral part of analyzing whether unoccupied areas are essential is to
begin with the occupied areas, but the Act does not require the
Services to first prove that the occupied areas are insufficient before
considering unoccupied areas. Therefore, we conclude that deleting
existing Sec. 424.12(e) restores the two parts of the statutory
definition (for occupied and unoccupied areas) to the relationship
envisioned by Congress.
As it is currently written, the provision in Sec. 424.12(e) also
confusingly references present range, while the two parts of the
statutory definition refer to the area occupied at the time of listing.
In practice, these concepts may be largely the same, given that
critical habitat ideally should be designated at or near the time of
listing. Nevertheless, the Services find that it will reduce confusion
to change the regulations to track the statutory distinction. In
addition, because critical habitat may be revised at any time, the
statutory distinction may be important during a revision, which could
occur several years after the listing of the species.
However, we note that unoccupied areas must be essential for the
conservation of the species, but need not have the features essential
to the conservation of the species: This follows directly from the
inclusion of the ``features essential'' language in section 3(5)(A)(i)
but not in section 3(5)(A)(ii). Thus, even keeping in mind that
``features'' may include features that support the occurrence of
ephemeral or dynamic habitat conditions, the Services may identify as
areas essential to the conservation of the species areas that do not
yet have the features, or degraded or successional areas that once had
the features, or areas that contain sources of or provide the processes
that maintain essential features in other areas. Areas may develop
features over time, or, through special management considerations or
protection. The conservation value may be influenced by the level of
effort needed to manage degraded habitat to the point where it could
support the listed species. Under Sec. 424.12(b)(2), the Services will
identify unoccupied areas, either with the features or not, that are
essential for the conservation of a species. This section is intended
to provide a flexible, rather than prescriptive, standard to allow the
Services to tailor the inquiry about what
[[Page 7435]]
is essential to the specific characteristics and circumstances of the
particular species.
The Services anticipate that critical habitat designations in the
future will likely increasingly use the authority to designate specific
areas outside the geographical area occupied by the species at the time
of listing following any generalized conservation strategy that might
be developed for the species. As the effects of global climate change
continue to influence distribution and migration patterns of species,
the ability to designate areas that a species has not historically
occupied is expected to become increasingly important. For example,
such areas may provide important connectivity between habitats, serve
as movement corridors, or constitute emerging habitat for a species
experiencing range shifts in latitude or altitude (such as to follow
available prey or host plants). Where the best available scientific
data suggest that specific unoccupied areas are, or it is reasonable to
determine from the record that they will eventually become, necessary
to support the species' recovery, it may be appropriate to find that
such areas are essential for the conservation of the species and thus
meet the definition of ``critical habitat.''
An example may clarify this situation: A butterfly depends on a
particular host plant. The host plant is currently found in a
particular area. The data show the host plant's range has been moving
up slope in response to warming temperatures (following the cooler
temperatures) resulting from the effects of climate change. Other
butterfly species have been documented to have shifted from their
historical ranges in response to changes in the range of host plants.
Therefore, we rationally conclude that the butterfly's range will
likely move up slope, and we would designate specific areas outside the
geographical area occupied by the butterfly at the time it was listed
if we concluded this area was essential based on this information.
Adherence to the process described above will ensure compliance
with the requirement in section 3(5)(C) of the Act, which states that,
except in those circumstances determined by the Secretary, critical
habitat shall not include the entire geographical area which can be
occupied by the threatened or endangered species.
Existing Sec. 424.12(c) resulted from a recent separate rulemaking
(77 FR 25611; May 1, 2012); it is not addressed in this rulemaking.
Section 424.12(d) includes minor language changes and removes the
example as it is not necessary for the text of the regulation.
We are removing current Sec. 424.12(e), as this concept--
designating specific areas outside the geographical area occupied by
the species at the time it is listed upon a determination by the
Secretary that such areas are essential for the conservation of the
species--is captured in revised Sec. 424.12(b)(2).
We are redesignating the current Sec. 424.12(f) as Sec. 424.12(e)
and adding a second sentence to emphasize that designation of critical
habitat for species that were listed prior to 1978 is at the discretion
of the Secretaries. The first sentence of Sec. 424.12(e) provides that
the Secretary ``may designate critical habitat for those species listed
as threatened or endangered species but for which no critical habitat
has been previously designated.'' This is substantially the same as
current Sec. 424.12(f) in the existing regulations, although the
Services have changed the passive voice to the active voice.
The new second sentence codifies in the regulations the principle
that the decision whether to designate critical habitat for species
listed prior to the effective date of the 1978 Amendments to the Act
(November 10, 1978) is at the discretion of the Secretary. This
principle is clearly reflected in the text of the statute and firmly
grounded in the legislative history. The definition of ``critical
habitat'' added to the Act in 1978 provided that the Secretary ``may,''
but was not required to, establish critical habitat for species already
listed by the effective date of the 1978 amendments. See Public Law 95-
632, 92 Stat. 3751 (Nov. 10, 1978) (codified at 16 U.S.C. 1532(5)(B));
see also Conservancy of Southwest Florida v. United States Fish &
Wildlife Service, No. 2:10-cv-106-FtM-SPC, 2011 WL 1326805, *9 (M.D.
Fla. April 6, 2011) (Florida panther) (plain language of statute
renders designation of habitat for species listed prior to the 1978
Amendments discretionary), aff'd, 677 F.3d 1073 (11th Cir. 2012); Fund
for Animals v. Babbitt, 903 F. Supp. 96, 115 n.8 (D.D.C. 1995) (grizzly
bear) (same). Similarly, the 1982 amendments expressly exempted species
listed prior to the 1978 amendments from the requirement that critical
habitat be designated concurrently with listing. See Public Law 97-304,
96 Stat. 1411, sec, 2(b)(4) (Oct. 13, 1982). To reduce potential
confusion, the revised regulations reflect the discretionary nature of
designations for such species.
As recent litigation has highlighted, the statutory history
regarding the procedures for undertaking proposals to designate
critical habitat for certain species is nuanced and has proven
confusing in other respects as well. For species listed before passage
of the 1982 amendments to the Act (October 13, 1982), any proposed
regulations issued by the Secretary to designate critical habitat are
governed by the provisions in section 4 of the Act applicable to
proposals to revise critical habitat designations. This is specified in
an uncodified provision of the 1982 amendments. See Public Law 97-304,
96 Stat. 1411, 1416, 2(b)(2), 16 U.S.C. 1533 (note) (``Any regulation
proposed after, or pending on, the date of the enactment of this Act to
designate critical habitat for a species that was determined before
such date of enactment to be endangered or threatened shall be subject
to the procedures set forth in section 4 of such Act of 1973 . . . for
regulations proposing revisions to critical habitat instead of those
for regulations proposing the designation of critical habitat.''); see
also Center for Biological Diversity v. FWS, 450 F.3d 930, 934-35 (9th
Cir. 2006) (unarmored three-spine stickleback). While the Services do
not propose to add regulatory text to address this narrow issue, we
explain below how these provisions must be understood within the
general scheme for designating critical habitat.
As a result of the above-referenced provision of the 1982
amendments, final regulations to designate critical habitat for species
that were listed prior to October 13, 1982, are governed by section
4(b)(6)(A)(i) of the Act. By contrast, for species listed after October
13, 1982, final regulations are governed by section 4(b)(6)(A)(ii).
Proposed rules for species listed both pre- and post-1982 are governed
by section 4(b)(5). Thus, the Services have additional options at the
final rule stage with regard to a proposal to designate critical
habitat for those species listed prior to 1982 that they do not have
when proposing to designate habitat for other species. These include an
option to make a finding that the revision ``should not be made'' and
to extend the 12-month deadline by an additional period of up to 6
months if there is substantial disagreement regarding the sufficiency
or accuracy of available data. See 16 U.S.C. 1533(b)(6)(B)(i); see also
Center for Biological Diversity, 450 F.3d at 936-37.
These provisions, however, do not affect the handling or
consideration of petitions seeking designation of critical habitat for
species listed prior to 1982. The term ``petition'' is not used in
section 2(b)(2) of the 1982 amendments to the Act (compare to section
2(b)(1) of the same amendments, which mentions
[[Page 7436]]
``[a]ny petition'' and ``any regulation''). Thus, the special
procedures for finalizing proposals to designate critical habitat for
species listed prior to 1982 come into play only upon a decision by the
Secretary to actually propose to designate critical habitat for such
species. Petitions seeking such designations are managed just like any
other petition seeking designation, which are governed by the
provisions of the Administrative Procedure Act rather than section 4 of
the Endangered Species Act. See 50 CFR 424.14(d); Conservancy of
Southwest Florida, 2011 WL 1326805, at *9 (``It is the Secretary's
proposal to designate critical habitat that triggers the statutory and
regulatory obligations, not plaintiffs' requests that the Secretary do
so.''); Fund for Animals v. Babbitt, 903 F. Supp. at 115 (petitions to
designate critical habitat are governed by the APA, not the ESA).
We are redesignating current Sec. 424.12(g) as Sec. 424.12(f)
with minor language changes.
We are redesignating current Sec. 424.12(h) as Sec. 424.12(g)
with minor language changes.
We are adding new Sec. 424.12(h). This paragraph reflects the
amendment to section 4(a)(3)(B)(i) of the Act in the National Defense
Authorization Act for Fiscal Year 2004 (Pub. L. 108-136). Section
424.12(h) codifies the amendments to the Act that prohibit the Services
from designating as critical habitat lands or other geographic areas
owned or controlled by the Department of Defense, or designated for its
use, if those lands are subject to an integrated natural resources
management plan (INRMP) prepared under section 101 of the Sikes Act (16
U.S.C. 670a), and if the Secretary determines in writing that such plan
provides a benefit to the species for which critical habitat is being
designated. In other words, if the Services conclude that an INRMP
``benefits'' the species, the area covered is ineligible for
designation. Unlike the Secretary's decision on exclusions under
section 4(b)(2) of the Act, this resulting exemption is not subject to
the discretion of the Secretary (once a benefit has been found).
Neither the Act nor the National Defense Authorization Act for
Fiscal Year 2004 defines the term ``benefit.'' However, the conference
report on the 2004 National Defense Authorization Act (Report 108-354)
instructed the Secretary to ``assess an INRMP's potential contribution
to species conservation, giving due regard to those habitat protection,
maintenance, and improvement projects . . . that address the particular
conservation and protection needs of the species for which critical
habitat would otherwise be proposed.'' We, therefore, conclude that
Congress intended ``benefit'' to mean ``conservation benefit.'' In
addition, because a finding of benefit results in an exemption from
critical habitat designation, and given the specific mention of
``habitat protection, maintenance, and improvement'' in the conference
report, we infer that Congress intended that an INRMP provide a
conservation benefit to the habitat (e.g., essential features) of the
species, in addition to the species. Examples of actions that provide
habitat-based conservation benefit to the species include: Reducing
fragmentation of habitat; maintaining or increasing populations in the
wild; planning for catastrophic events; protecting, enhancing, or
restoring habitats; buffering protected areas; and testing and
implementing new habitat-based conservation strategies.
In the conference report, Congress further instructed the Secretary
to ``establish criteria that would be used to determine if an INRMP
benefits the listed species.'' The Services, therefore, describe in
Sec. 424.12(h) some factors that will help us determine whether an
INRMP provides a conservation benefit: (1) The extent of area and
features present; (2) the type and frequency of use of the area by the
species; (3) the relevant elements of the INRMP in terms of management
objectives, activities covered, and best management practices, and the
certainty that the relevant elements will be implemented; and (4) the
degree to which the relevant elements of the INRMP will protect the
habitat from the types of effects that would be addressed through a
destruction-or-adverse-modification analysis. FWS will defer to our
Guidelines for Coordination on Integrated Natural Resource Management
Plans in evaluating these plans.
Under the Sikes Act, the Department of Defense is also instructed
to prepare INRMPs in cooperation with FWS and each appropriate State
fish and wildlife agency. The compliant or operational INRMP must
reflect the mutual agreement of the involved agencies on the
conservation, protection, and management of fish and wildlife
resources. In other words, FWS must agree with an INRMP (reflected by
signature of the plan or letter of concurrence pursuant to the Sikes
Act (not to be confused with a letter of concurrence issued in relation
to consultation under section 7(a)(2) of the Act)) before an INRMP can
be relied upon for making an area ineligible for designation under
section 4(a)(3)(B)(i). As part of this process, FWS will also conduct
consultation under section 7(a)(2) of the Act, if listed species or
designated critical habitat may be affected by the actions included in
the INRMP. Section 7(a)(2) of the Act will continue to apply to any
Federal actions affecting the species once an INRMP is compliant or
operation. However, if the area is ineligible for critical habitat
designation under section 4(a)(3)(B)(i), then those consultations would
address only effects to the species and the likelihood of the Federal
action to jeopardize the continued existence of the species.
New Sec. 424.12(h) specifies that an INRMP must be compliant or
operational to make an area ineligible for designation under section
4(a)(3)(B)(i). When the Department of Defense provides a draft INRMP
for the Services' consideration during development of a critical
habitat designation, the Services may evaluate it following the
guidelines set forth in our Policy on Exclusions from Critical Habitat
under Section 4(b)(2) of the Act.
Existing Sec. 424.19 results from a recent, separate rulemaking
(78 FR 53058), and is not addressed in this rulemaking.
Required Determinations
Regulatory Planning and Review--Executive Orders 12866 and 13563
Executive Order 12866 provides that the Office of Information and
Regulatory Affairs (OIRA) in the Office of Management and Budget will
review all significant rules. The Office of Information and Regulatory
Affairs has determined that this rule is significant.
Executive Order 13563 reaffirms the principles of E.O. 12866 while
calling for improvements in the nation's regulatory system to promote
predictability, to reduce uncertainty, and to use the best, most
innovative, and least burdensome tools for achieving regulatory ends.
The executive order directs agencies to consider regulatory approaches
that reduce burdens and maintain flexibility and freedom of choice for
the public where these approaches are relevant, feasible, and
consistent with regulatory objectives. 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.
[[Page 7437]]
Regulatory Flexibility Act
Under the Regulatory Flexibility Act (as amended by the Small
Business Regulatory Enforcement Fairness Act (SBREFA) of 1996; 5 U.S.C.
601 et seq.), whenever a Federal 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 entities (i.e., small
businesses, small organizations, and small government jurisdictions).
However, no regulatory flexibility analysis is required if the head of
an agency, or his designee, certifies that the rule will 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 a statement of the factual basis for certifying
that a rule will not have a significant economic impact on a
substantial number of small entities. We certified that the proposed
rule to implement these changes to the 50 CFR part 424 regulations
would not have a significant economic impact on a substantial number of
small entities (79 FR 27066, at 27075). Several commenters objected to
the Services' determination that a regulatory flexibility analysis is
not required for this regulation, stating the regulated community is
affected by this regulation. We explained that NMFS and FWS are the
only entities that are directly affected by this rule because we are
the only entities that designate critical habitat, and this rule
pertains to the procedures for carrying out those designations (See our
response to Comment 81). No external entities, including any small
businesses, small organizations, or small governments, will experience
any direct economic impacts from this rule. No information received
during the public comment period leads us to change our analysis.
Unfunded Mandates Reform Act (2 U.S.C. 1501 et seq.)
In accordance with the Unfunded Mandates Reform Act (2 U.S.C. 1501
et seq.):
(a) On the basis of information contained in the ``Regulatory
Flexibility Act'' section above, these regulations will not
``significantly or uniquely'' affect small governments. We have
determined and certify pursuant to the Unfunded Mandates Reform Act, 2
U.S.C. 1502, that these regulations will not impose a cost of $100
million or more in any given year on local or State governments or
private entities. A Small Government Agency Plan is not required. As
explained above, small governments will not be affected because the
regulations will not place additional requirements on any city, county,
or other local municipalities.
(b) These regulations will not produce a Federal mandate on State,
local, or tribal governments or the private sector of $100 million or
greater in any year; that is, this rule is not a ``significant
regulatory action'' under the Unfunded Mandates Reform Act. These
regulations will impose no obligations on State, local, or tribal
governments.
Takings (E.O. 12630)
In accordance with Executive Order 12630, these regulations will
not have significant takings implications. These regulations will not
pertain to ``taking'' of private property interests, nor will they
directly affect private property. A takings implication assessment is
not required because these regulations (1) will not effectively compel
a property owner to suffer a physical invasion of property and (2) will
not deny all economically beneficial or productive use of the land or
aquatic resources. These regulations will substantially advance a
legitimate government interest (conservation and recovery of endangered
and threatened species) and will not present a barrier to all
reasonable and expected beneficial use of private property.
Federalism (E.O. 13132)
In accordance with Executive Order 13132, we have considered
whether these regulations will have significant Federalism effects and
have determined that a Federalism assessment is not required. These
regulations pertain only to determinations to designate critical
habitat under section 4 of the Act, and will not have substantial
direct effects on the States, on the relationship between the Federal
Government and the States, or on the distribution of power and
responsibilities among the various levels of government.
Civil Justice Reform (E.O. 12988)
These regulations do not unduly burden the judicial system and meet
the applicable standards provided in sections 3(a) and 3(b)(2) of
Executive Order 12988. These regulations will clarify how the Services
will make designations of critical habitat under section 4 of the Act.
Government-to-Government Relationship With Tribes
In accordance with Executive Order 13175 ``Consultation and
Coordination with Indian Tribal Governments,'' the Department of the
Interior's manual at 512 DM 2, and the Department of Commerce (DOC)
Tribal Consultation and Coordination Policy''/(May 21, 2013), DOC
Departmental Administrative Order (DAO) 218-8, and NOAA Administrative
Order (NAO) 218-8 (April 2012), we have considered possible effects of
this final rule on federally recognized Indian Tribes. Following an
exchange of information with tribal representatives, we have determined
that this rule, which modifies the general framework for designating
critical habitat under the ESA, does not have tribal implications as
defined in Executive Order 13175. We will continue to collaborate/
coordinate with tribes on issues related to federally listed species
and their habitats and work with them as appropriate as we develop
particular critical habitat designations, including consideration of
potential exclusion on the basis of tribal interests. See Joint
Secretarial Order 3206 (``American Indian Tribal Rights, Federal-Tribal
Trust Responsibilities, and the Endangered Species Act'', June 5,
1997).
Paperwork Reduction Act
This rule does not contain any new collections of information that
require approval by the OMB under the Paperwork Reduction Act. This
rule will not impose recordkeeping or reporting requirements on State
or local governments, individuals, businesses, or organizations. An
agency 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.
National Environmental Policy Act
We have analyzed these regulations in accordance with the criteria
of the National Environmental Policy Act (NEPA), the Department of the
Interior regulations on Implementation of the National Environmental
Policy Act (43 CFR 46.10-46.450), the Department of the Interior Manual
(516 DM 1-6 and 8)), and National Oceanic and Atmospheric
Administration (NOAA) Administrative Order 216-6. Our analysis includes
evaluating whether this action is procedural, administrative, or legal
in nature and, therefore, a categorical exclusion applies.
Following a review of the changes to the regulations at 50 CFR
424.01, 424.02, and 424.12 and our requirements under NEPA, we find
that the categorical exclusion found at 43 CFR 46.210(i) applies to
these regulation changes. At 43 CFR 46.210(i), the Department of the
Interior has found that the following category of actions
[[Page 7438]]
would not individually or cumulatively have a significant effect on the
human environment and are, therefore, categorically excluded from the
requirement for completion of an environmental assessment or
environmental impact statement:
``Policies, directives, regulations, and guidelines: that are of an
administrative, financial, legal, technical, or procedural nature.''
NOAA Administrative Order 216-6 contains a substantively identical
exclusion for ``policy directives, regulations and guidelines of an
administrative, financial, legal, technical or procedural nature.''
Sec. 6.03c.3(i).
At the time DOI's categorical exclusion was promulgated, there was
no preamble language that would assist in interpreting what kinds of
actions fall within the categorical exclusion. However, in 2008, the
preamble for a language correction to this categorical exclusion gave
as an example of an action that would fall within the exclusion the
issuance of guidance to applicants for transferring funds
electronically to the Federal Government. In addition, examples of
recent Federal Register notices invoking this categorical exclusion
include a final rule that established the timing requirements for the
submission of a Site Assessment Plan or General Activities Plan for a
renewable energy project on the Outer Continental Shelf (78 FR 12676;
February 26, 2013), a final rule that established limited liability for
Noncoal Reclamation by Certified States and Indian Tribes (78 FR 8822;
February 6, 2013), and a final rule changing the tenure of eagle
permits (77 FR 22267; April 13, 2012). These regulations fell within
the categorical exclusion because they did not result in any
substantive change. In no way did they alter the standards for, or
outcome of, any physical or regulatory Federal actions.
The changes to the critical habitat designation criteria are
similar to these examples of actions that are fundamentally
administrative, technical, and procedural in nature. The changes to the
regulations at 50 CFR 424.01, 424.02, and 424.12 (except for paragraph
(c)) clarify the procedures and criteria used for designating critical
habitat, addressing in particular several key issues that have been
subject to frequent litigation. In addition, the regulation revisions
to 50 CFR 424.01, 424.02, and 424.12 better track the statutory
language of the Act and make transparent practices the Services follow
as a result of case law. The Services also make minor wording and
formatting revisions throughout the three sections to reflect plain
language standards. The regulation revision as a whole carries out the
requirements of Executive Order 13563 because, in this rule, the
Services have analyzed existing rules retrospectively ``to make the
agencies' regulatory program more effective or less burdensome in
achieving the regulatory objectives.'' None of the changes to the text
of the regulation will result in changes to the opportunity for public
involvement in any critical habitat designations.
We also considered whether any ``extraordinary circumstances''
apply to this situation, such that the DOI categorical exclusion would
not apply. See 43 CFR 46.215 (``Categorical Exclusions: Extraordinary
Circumstances''). We determined that no extraordinary circumstances
apply. Although the final regulations would revise the implementing
regulations for section 4 of the Act, the effects of these proposed
changes would not ``have significant impacts on species listed, or
proposed to be listed, on the List of Endangered or Threatened Species
or have significant impacts on designated Critical Habitat for these
species,'' as nothing in the revised regulations is intended to require
that any previously listed species or completed critical habitat
designation be reevaluated on this basis. Furthermore, the revised
regulations do not ``[e]stablish a precedent for future action or
represent a decision in principle about future actions with potentially
significant environmental effects'' (43 CFR 46.215(e)). None of the
extraordinary circumstances in 43 CFR 46.215(a) through (l) apply to
the revised regulations in 50 CFR 424.01, 424.02, or 424.12.
Nor would the final regulations trigger any of the extraordinary
circumstances of NAO 216-6. This rule does not involve a geographic
area with unique characteristics, is not the subject of public
controversy based on potential environmental consequences, will not
result in uncertain environmental impacts or unique or unknown risks,
does not establish a precedent or decision in principle about future
proposals, will not have significant cumulative impacts, and will not
have any adverse effects upon endangered or threatened species or their
habitats. Sec. 5.05c.
We completed an Environmental Action Statement for the Categorical
Exclusion for the revised regulations in 50 CFR 424.01, 424.02, and
424.12.
Energy Supply, Distribution or Use (E.O. 13211)
Executive Order 13211 requires agencies to prepare Statements of
Energy Effects when undertaking certain actions. These regulations are
not expected to affect energy supplies, distribution, and use.
Therefore, this action is a not a significant energy action, and no
Statement of Energy Effects is required.
References Cited
A complete list of all references cited in this document is
available on the Internet at https://www.regulations.gov or upon request
from the U.S. Fish and Wildlife Service (see FOR FURTHER INFORMATION
CONTACT).
Authority
We are taking this action under the authority of the Endangered
Species Act of 1973, as amended (16 U.S.C. 1531 et seq.).
List of Subjects in 50 CFR Part 424
Administrative practice and procedure, Endangered and threatened
species.
Regulation Promulgation
Accordingly, we are amending part 424, subchapter A of chapter IV,
title 50 of the Code of Federal Regulations, as set forth below:
PART 424--[AMENDED]
0
1. The authority citation for part 424 continues to read as follows:
Authority: 16 U.S.C. 1531 et seq.
0
2. Revise Sec. 424.01 to read as follows:
Sec. 424.01 Scope and purpose.
(a) Part 424 provides regulations for revising the Lists of
Endangered and Threatened Wildlife and Plants and designating or
revising the critical habitats of listed species. Part 424 provides
criteria for determining whether species are endangered or threatened
species and for designating critical habitats. Part 424 also
establishes procedures for receiving and considering petitions to
revise the lists and for conducting periodic reviews of listed species.
(b) The purpose of the regulations in part 424 is to interpret and
implement those portions of the Act that pertain to the listing of
species as threatened or endangered species and the designation of
critical habitat.
0
3. Revise Sec. 424.02 to read as follows:
Sec. 424.02 Definitions.
The definitions contained in the Act and parts 17, 222, and 402 of
this title
[[Page 7439]]
apply to this part, unless specifically modified by one of the
following definitions. Definitions contained in part 17 of this title
apply only to species under the jurisdiction of the U.S. Fish and
Wildlife Service. Definitions contained in part 222 of this title apply
only to species under the jurisdiction of the National Marine Fisheries
Service.
Candidate. Any species being considered by the Secretary for
listing as an endangered or threatened species, but not yet the subject
of a proposed rule.
Conserve, conserving, and conservation. To use and the use of all
methods and procedures that are necessary to bring any endangered or
threatened species to the point at which the measures provided pursuant
to the Act are no longer necessary, i.e., the species is recovered in
accordance with Sec. 402.02 of this chapter. Such methods and
procedures include, but are not limited to, all activities associated
with scientific resources management such as research, census, law
enforcement, habitat acquisition and maintenance, propagation, live
trapping, and transplantation, and, in the extraordinary case where
population pressures within a given ecosystem cannot be otherwise
relieved, may include regulated taking.
Geographical area occupied by the species. An area that may
generally be delineated around species' occurrences, as determined by
the Secretary (i.e., range). Such areas may include those areas used
throughout all or part of the species' life cycle, even if not used on
a regular basis (e.g., migratory corridors, seasonal habitats, and
habitats used periodically, but not solely by vagrant individuals).
List or lists. The Lists of Endangered and Threatened Wildlife and
Plants found at 50 CFR 17.11(h) or 17.12(h).
Physical or biological features. The features that support the
life-history needs of the species, including but not limited to, water
characteristics, soil type, geological features, sites, prey,
vegetation, symbiotic species, or other features. A feature may be a
single habitat characteristic, or a more complex combination of habitat
characteristics. Features may include habitat characteristics that
support ephemeral or dynamic habitat conditions. Features may also be
expressed in terms relating to principles of conservation biology, such
as patch size, distribution distances, and connectivity.
Public hearing. An informal hearing to provide the public with the
opportunity to give comments and to permit an exchange of information
and opinion on a proposed rule.
Special management considerations or protection. Methods or
procedures useful in protecting the physical or biological features
essential to the conservation of listed species.
Species. Includes any species or subspecies of fish, wildlife, or
plant, and any distinct population segment of any vertebrate species
that interbreeds when mature. Excluded is any species of the Class
Insecta determined by the Secretary to constitute a pest whose
protection under the provisions of the Act would present an
overwhelming and overriding risk to man.
Wildlife or fish and wildlife. Any member of the animal kingdom,
including without limitation, any vertebrate, mollusk, crustacean,
arthropod, or other invertebrate, and includes any part, product, egg,
or offspring thereof, or the dead body or parts thereof.
0
4. In Sec. 424.12, revise paragraphs (a), (b), and (d) through (h) to
read as follows:
Sec. 424.12 Criteria for designating critical habitat.
(a) To the maximum extent prudent and determinable, we will propose
and finalize critical habitat designations concurrent with issuing
proposed and final listing rules, respectively. If designation of
critical habitat is not prudent or if critical habitat is not
determinable, the Secretary will state the reasons for not designating
critical habitat in the publication of proposed and final rules listing
a species. The Secretary will make a final designation of critical
habitat on the basis of the best scientific data available, after
taking into consideration the probable economic, national security, and
other relevant impacts of making such a designation in accordance with
Sec. 424.19.
(1) A designation of critical habitat is not prudent when any of
the following situations exist:
(i) The species is threatened by taking or other human activity,
and identification of critical habitat can be expected to increase the
degree of such threat to the species; or
(ii) Such designation of critical habitat would not be beneficial
to the species. In determining whether a designation would not be
beneficial, the factors the Services may consider include but are not
limited to: Whether the present or threatened destruction,
modification, or curtailment of a species' habitat or range is not a
threat to the species, or whether any areas meet the definition of
``critical habitat.''
(2) Designation of critical habitat is not determinable when one or
both of the following situations exist:
(i) Data sufficient to perform required analyses are lacking; or
(ii) The biological needs of the species are not sufficiently well
known to identify any area that meets the definition of ``critical
habitat.''
(b) Where designation of critical habitat is prudent and
determinable, the Secretary will identify specific areas within the
geographical area occupied by the species at the time of listing and
any specific areas outside the geographical area occupied by the
species to be considered for designation as critical habitat.
(1) The Secretary will identify, at a scale determined by the
Secretary to be appropriate, specific areas within the geographical
area occupied by the species for consideration as critical habitat. The
Secretary will:
(i) Identify the geographical area occupied by the species at the
time of listing.
(ii) Identify physical and biological features essential to the
conservation of the species at an appropriate level of specificity
using the best available scientific data. This analysis will vary
between species and may include consideration of the appropriate
quality, quantity, and spatial and temporal arrangements of such
features in the context of the life history, status, and conservation
needs of the species.
(iii) Determine the specific areas within the geographical area
occupied by the species that contain the physical or biological
features essential to the conservation of the species.
(iv) Determine which of these features may require special
management considerations or protection.
(2) The Secretary will identify, at a scale determined by the
Secretary to be appropriate, specific areas outside the geographical
area occupied by the species that are essential for its conservation,
considering the life history, status, and conservation needs of the
species based on the best available scientific data.
* * * * *
(d) When several habitats, each satisfying the requirements for
designation as critical habitat, are located in proximity to one
another, the Secretary may designate an inclusive area as critical
habitat.
(e) The Secretary may designate critical habitat for those species
listed as threatened or endangered but for which no critical habitat
has been previously designated. For species listed prior to November
10, 1978, the designation of
[[Page 7440]]
critical habitat is at the discretion of the Secretary.
(f) The Secretary may revise existing designations of critical
habitat according to procedures in this section as new data become
available.
(g) The Secretary will not designate critical habitat within
foreign countries or in other areas outside of the jurisdiction of the
United States.
(h) The Secretary will not designate as critical habitat land or
other geographic areas owned or controlled by the Department of
Defense, or designated for its use, that are subject to a compliant or
operational integrated natural resources management plan (INRMP)
prepared under section 101 of the Sikes Act (16 U.S.C. 670a) if the
Secretary determines in writing that such plan provides a conservation
benefit to the species for which critical habitat is being designated.
In determining whether such a benefit is provided, the Secretary will
consider:
(1) The extent of the area and features present;
(2) The type and frequency of use of the area by the species;
(3) The relevant elements of the INRMP in terms of management
objectives, activities covered, and best management practices, and the
certainty that the relevant elements will be implemented; and
(4) The degree to which the relevant elements of the INRMP will
protect the habitat from the types of effects that would be addressed
through a destruction-or-adverse-modification analysis.
Dated: January 29, 2016.
Michael J. Bean,
Principal Deputy Assistant Secretary for Fish and Wildlife and Parks.
Dated: January 29, 2016.
Samuel D. Rauch, III,
Deputy Assistant Administrator for Regulatory Programs, National Marine
Fisheries Service.
[FR Doc. 2016-02680 Filed 2-10-16; 8:45 am]
BILLING CODE 4310-55-P; 3510-22-P