Listing Endangered or Threatened Species: Amendment to the Endangered Species Act Listing of the Southern Resident Killer Whale Distinct Population Segment, 7380-7390 [2015-02604]
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Federal Register / Vol. 80, No. 27 / Tuesday, February 10, 2015 / Rules and Regulations
(n) Training. (1) A program must train
all governing body, policy council,
management, and staff who determine
eligibility on applicable Federal
regulations and program policies and
procedures. Training must, at a
minimum:
(i) Include methods on how to collect
complete and accurate eligibility
information from families and third
party sources;
(ii) Incorporate strategies for treating
families with dignity and respect and
for dealing with possible issues of
domestic violence, stigma, and privacy;
and,
(iii) Explain program policies and
procedures that describe actions taken
against staff, families, or participants
who intentionally attempt to provide or
provide false information.
(2) A program must train management
and staff members who make eligibility
determinations within 90 days
following the effective date of this rule,
and as soon as possible, but within 90
days of hiring new staff after the initial
training has been conducted.
(3) A program must train all governing
body and policy council members
within 180 days following the effective
date of this rule, and within 180 days of
the beginning of the term of a new
governing body or policy council
member after the initial training has
been conducted.
(4) A program must develop policies
on how often training will be provided
after the initial training.
[FR Doc. 2015–02491 Filed 2–9–15; 8:45 am]
BILLING CODE P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 224
[Docket No. 130321272–5109–03]
RIN 0648–XC589
Listing Endangered or Threatened
Species: Amendment to the
Endangered Species Act Listing of the
Southern Resident Killer Whale
Distinct Population Segment
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
rljohnson on DSK3VPTVN1PROD with RULES
AGENCY:
On January 25, 2013, we,
NMFS, received a petition submitted by
the People for the Ethical Treatment of
Animals Foundation to remove the
SUMMARY:
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exclusion of captive animals from the
endangered species listing of Southern
Resident killer whale DPS, as well as,
recognize the captive killer whale
(Orcinus orca) ‘‘Lolita’’ as a protected
member of the endangered Southern
Resident killer whale Distinct
Population Segment (DPS). We
completed a status review and
published a proposed rule, and we are
now amending the regulatory language
of the Endangered Species Act (ESA)
listing of the DPS by removing the
exclusion for captive members of the
population. We have further determined
that Lolita, a female killer whale
captured from the Southern Resident
killer whale population in 1970 who
resides at the Miami Seaquarium in
Miami, Florida, is not excluded from the
Southern Resident killer whale DPS due
to her captive status.
We proposed to amend the regulatory
language of the ESA listing to remove
the exclusion for captive whales from
the Southern Resident killer whale DPS
on January 27, 2014. Additionally, we
solicited scientific and commercial
information pertaining to the proposed
rule and also conducted a peer review
of the status review information on
Lolita that informed the proposed rule.
We have determined that captive
members of the Southern Resident killer
whale population should be included in
the listed Southern Resident killer
whale DPS. This rule amends the
regulatory language of the listing to
remove the exclusion for captive
members of the DPS.
DATES: This final rule becomes effective
on May 11, 2015.
ADDRESSES: Information supporting this
final rule can be found on our Web site
at: https://
www.westcoast.fisheries.noaa.gov/
protected_species/marine_mammals/
killer_whale/lolita_petition.html.
Or in our office at:
• Protected Resources Division,
NMFS, Northwest Region, Protected
Resources Division, 7600 Sand Point
Way NE., Attention Lynne Barre, Branch
Chief.
FOR FURTHER INFORMATION CONTACT:
Lynne Barre, NMFS Northwest Region,
(206) 526–4745; Marta Nammack, NMFS
Office of Protected Resources, (301)
427–8469.
SUPPLEMENTARY INFORMATION:
ESA Statutory Provisions and Policy
Considerations
On January 25, 2013, we received a
petition submitted by the People for the
Ethical Treatment of Animals
Foundation on behalf of the Animal
Legal Defense Fund, Orca Network,
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Howard Garrett, Shelby Proie, Karen
Munro, and Patricia Sykes to remove the
exclusion of captive whales from the
SRKW DPS ESA listing and to include
the killer whale known as Lolita in the
ESA listing of the Southern Resident
killer whales. Lolita is a female killer
whale captured from the Southern
Resident population in 1970, who
currently resides at the Miami
Seaquarium in Miami, Florida. Copies
of the petition are available upon
request (see ADDRESSES, above).
In accordance with section 4(b)(3)(A)
of the ESA, to the maximum extent
practicable within 90 days of receipt of
a petition to list, reclassify, or delist a
species, the Secretary of Commerce is
required to make a finding on whether
that petition presents substantial
scientific or commercial information
indicating that the petitioned action
may be warranted, and to promptly
publish such finding in the Federal
Register (16 U.S.C. 1533(b)(3)(A)). The
Secretary of Commerce has delegated
this duty to NMFS. If we find that the
petition presents substantial
information indicating that the
petitioned action may be warranted, we
must commence a review of the status
of the species concerned, during which
we will conduct a comprehensive
review of the best available scientific
and commercial information. On April
29, 2013 we made a finding (78 FR
25044) that there was sufficient
information indicating that the
petitioned action may be warranted and
requested comments to inform a status
review.
After accepting a petition and
initiating a status review, within 12
months of receipt of the petition we
must conclude the review with a
determination that the petitioned action
is not warranted, or a proposed
determination that the action is
warranted. Under specific facts, we may
also issue a determination that the
action is warranted but precluded. On
January 27, 2014 we made a finding (79
FR 4313) that the petitioned action to
remove the exclusion of captive killer
whales from the ESA listing of the
Southern Resident killer whale DPS and
to include captive killer whales in the
ESA listing of the Southern Resident
killer whale DPS was warranted and
proposed to amend the regulatory
language describing the DPS by
removing the current exclusion for
captive whales. Within 12 months of
issuing a proposed rule on a listing
determination, we must publish a final
regulation to implement the
determination or publish a notice
extending the 12-month period. This
notice is a final rule to implement our
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Federal Register / Vol. 80, No. 27 / Tuesday, February 10, 2015 / Rules and Regulations
determination that the petitioned action
is warranted and to amend the language
describing the endangered listing of the
Southern Resident killer whale DPS by
removing the exclusion for captive
whales.
Under the ESA, the term ‘‘species’’
means a species, a subspecies, or a DPS
of a vertebrate species (16 U.S.C.
1532(16)). A joint NMFS-U.S. Fish and
Wildlife (USFWS) policy clarifies the
Services’ interpretation of the phrase
‘‘Distinct Population Segment,’’ or DPS
(61 FR 4722; February 7, 1996). The DPS
Policy requires the consideration of two
elements when evaluating whether a
vertebrate population segment qualifies
as a DPS under the ESA: (1)
Discreteness of the population segment
in relation to the remainder of the
species/taxon, and, if discrete; (2) the
significance of the population segment
to the species/taxon.
A species is ‘‘endangered’’ if it is in
danger of extinction throughout all or a
significant portion of its range, and
‘‘threatened’’ if it is likely to become
endangered within the foreseeable
future throughout all or a significant
portion of its range (ESA sections 3(6)
and 3(20), respectively, 16 U.S.C.
1532(6) and (20)). Thus, we interpret an
‘‘endangered species’’ to be one that is
presently in danger of extinction. A
‘‘threatened species,’’ on the other hand,
is not presently in danger of extinction,
but is likely to become so in the
foreseeable future (that is, at a later
time). In other words, the primary
statutory difference between a
threatened species and an endangered
species is the timing of when a species
may be in danger of extinction, either
presently (endangered) or in the
foreseeable future (threatened). Pursuant
to the ESA and our implementing
regulations, we determine whether a
species is threatened or endangered
based on any one or a combination of
the following section 4(a)(1) factors: the
present or threatened destruction,
modification, or curtailment of habitat
or range; overutilization for commercial,
recreational, scientific, or educational
purposes; disease or predation;
inadequacy of existing regulatory
mechanisms; and any other natural or
manmade factors affecting the species’
existence (16 U.S.C. 1533(a)(1), 50 CFR
424.11(c)).
We make listing determinations based
on the best available scientific and
commercial data available after
conducting a review of the status of the
species and after taking into account
efforts being made by any State or
foreign nation or political subdivision
thereof to protect the species.
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Background
Three distinct forms or ecotypes of
killer whales, termed residents,
transients, and offshores, are recognized
in the northeastern Pacific Ocean.
Resident killer whales in U.S. waters are
distributed from Alaska to California,
with four distinct populations:
Southern, Northern, Southern Alaska,
and Western Alaska (Krahn et al., 2002;
2004). Resident killer whales are fish
eaters and live in stable matrilineal
pods. The West Coast transient killer
whales have a different social structure,
are found in smaller groups, and eat
marine mammals. Offshore killer whales
are found in large groups, and their diet
is presumed to consist primarily of fish,
including sharks. While the ranges of
the different ecotypes of whales overlap
in the northeastern Pacific Ocean,
available genetic data indicate that there
is a high degree of reproductive
isolation among residents, transients,
and offshores (Krahn et al., 2004; NMFS,
2013).
The Southern Resident killer whale
population consists of three pods,
identified as J, K, and L pods, that reside
for part of the year in the inland
waterways of Washington State and
British Columbia (Strait of Georgia,
Strait of Juan de Fuca, and Puget
Sound), principally during the late
spring, summer, and fall (NMFS, 2008).
Pods visit coastal sites off Washington
and Vancouver Island, and travel as far
south as central California and as far
north as Southeast Alaska (Ford et al.,
2000; NMFS, 2008; Department of
Fisheries and Oceans, unpublished
data).
In 2001 we received a petition to list
the Southern Resident killer whale
population as threatened or endangered
under the ESA (CBD, 2001) and we
formed a Biological Review Team (BRT)
to assist with a status review (NMFS,
2002). After conducting the status
review, we determined that listing the
Southern Resident killer whale
population as a threatened or
endangered species was not warranted
because the science at that time did not
support identifying the Southern
Resident killer whale population as a
DPS as defined by the ESA (67 FR
44133; July 1, 2002). Because of the
uncertainties regarding killer whale
taxonomy (i.e., whether killer whales
globally should be considered as one
species or as multiple species and/or
subspecies), we announced that we
would reconsider the taxonomy of killer
whales within 4 years. Following the
determination, the Center for Biological
Diversity and other plaintiffs challenged
our ‘‘not warranted’’ finding under the
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ESA in U.S. District Court. The U.S.
District Court for the Western District of
Washington issued an order on
December 17, 2003, which set aside our
‘‘not warranted’’ finding and remanded
the matter to us for redetermination of
whether the Southern Resident killer
whale population should be listed
under the ESA (Center for Biological
Diversity v. Lohn, 296 F. Supp. 2d. 1223
(W.D. Wash. 2003)). The court found
that where there is ‘‘compelling
evidence that the global Orcinus orca
taxon is inaccurate,’’ the agency may not
rely on ‘‘a lack of consensus in the field
of taxonomy regarding the precise,
formal taxonomic redefinition of killer
whales.’’ As a result of the court’s order,
we co-sponsored a Cetacean Taxonomy
workshop in 2004, which included a
special session on killer whales, and
reconvened a BRT to prepare an
updated status review document for
Southern Resident killer whales (NMFS,
2004).
The BRT agreed that the Southern
Resident killer whale population likely
belongs to an unnamed subspecies of
resident killer whales in the North
Pacific, which includes the Southern
and Northern Residents, as well as the
resident killer whales of Southeast
Alaska, Prince William Sound, Kodiak
Island, the Bering Sea and Russia (but
not transients or offshores). The BRT
concluded that the Southern Resident
killer whale population is discrete from
other populations within the North
Pacific Resident taxon and significant
with respect to the North Pacific
Resident taxon and therefore should be
considered a DPS. In addition, the BRT
conducted a population viability
analysis, which modeled the probability
of species extinction under a range of
assumptions. Based on the findings of
the status review and an evaluation of
the factors affecting the DPS, we
published a proposed rule to list the
Southern Resident killer whale DPS as
threatened on December 22, 2004 (69 FR
76673). After considering public
comments on the proposed rule and
other available information, we
reconsidered the status of the Southern
Resident killer whale DPS and issued a
final rule to list the Southern Resident
killer whale DPS as endangered on
November 18, 2005 (70 FR 69903). The
regulatory language in the listing
limited the DPS to whales from J, K and
L pods, wherever they are found in the
wild, and not including Southern
Resident killer whales placed in
captivity prior to listing or their captive
born progeny.
Following the listing, we designated
critical habitat, completed a recovery
plan, and conducted a 5-year review for
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the Southern Resident killer whale DPS.
We issued a final rule designating
critical habitat for the Southern
Resident killer whale DPS on November
29, 2006 (71 FR 69055). After engaging
stakeholders and providing multiple
drafts for public comment, we
announced the Final Recovery Plan for
the Southern Resident killer whale DPS
on January 24, 2008 (73 FR 4176). We
have continued working with partners
to implement actions in the recovery
plan. In March 2011, we completed a 5year review of the ESA status of the
Southern Resident killer whale DPS,
concluding that no change was needed
in its listing status and that the
Southern Resident killer whale DPS
would remain listed as endangered
(NMFS, 2011). The 5-year review also
noted that there was no relevant new
information for this species regarding
the application of the DPS policy.
On August 2, 2012, we received a
petition submitted by the Pacific Legal
Foundation on behalf of the Center for
Environmental Science Accuracy and
Reliability, Empresas Del Bosque, and
Coburn Ranch to delist the endangered
Southern Resident killer whale DPS
under the ESA. We made a 90-day
finding accepting the petition and
soliciting information to inform a status
review (77 FR 70733; November 27,
2012). Based on a review of the
scientific information (NWFSC, 2013)
and our full status review, we issued a
12-month finding on August 5, 2013,
that the petitioned action was not
warranted and the Southern Resident
killer whale DPS remains listed as
endangered (78 FR 47277).
Lolita Petition
On January 25, 2013, we received a
petition submitted by the People for the
Ethical Treatment of Animals
Foundation on behalf of the Animal
Legal Defense Fund, Orca Network,
Howard Garrett, Shelby Proie, Karen
Munro, and Patricia Sykes to remove the
exclusion of captive killer whales from
the ESA listing of the Southern Resident
Killer Whale DPS and to include the
killer whale known as Lolita in the ESA
listing of the Southern Resident killer
whales. The petition described Lolita, a
female killer whale captured from the
Southern Resident population in 1970,
who currently resides at the Miami
Seaquarium in Miami, Florida, as the
only remaining member of the Southern
Residents alive in captivity. The
petitioners presented information about
Lolita’s origin and contended that Lolita
is a member of the endangered Southern
Resident DPS and should be included
within the ESA listing. In addition, they
provided a legal argument that ‘‘the ESA
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applies to captive members of listed
species’’ and asserted that ‘‘NMFS has a
non-discretionary duty to include Lolita
in the listing of the Southern Resident
killer whales under the ESA.’’ The
petition also included information about
how each of the five section 4(a)(1)
factors applies with respect to Lolita.
Lastly, the petitioners contended that
including Lolita in the ESA listing will
contribute to conservation of the wild
Southern Resident killer whale
population.
On April 29, 2013, we found that the
information contained in the petition,
viewed in the context of information
readily available in our files, presented
substantial scientific information that
would lead a reasonable person to
believe the petitioned action may be
warranted (78 FR 25044). We noted that
the information on Lolita’s genetic
heritage and consideration of captive
individuals under the ESA provided a
basis for us to accept the petition. The
petition included an assessment of how
listing Lolita would help conserve the
wild Southern Resident population and
also a review of the 4(a)(1) factors
described earlier and considered in
listing determinations. Our 90-day
finding accepting the petition, however,
was based on the biological information
regarding Lolita’s genetic heritage and
consideration of the applicability of the
ESA to captive members of endangered
species. Our review of Lolita’s status
with respect to the Southern Resident
killer whale DPS similarly focused on
these two aspects and did not include
a review of the Section 4(a)(1) factors for
Lolita or the wild population. Our status
review considered the best available
information including information
received through the public comment
period, a review of scientific
information conducted by our
Northwest Fisheries Science Center,
including published peer-reviewed
journal articles and unpublished
scientific reports, and information in the
petition.
Upon publishing our 90-day finding
accepting the petition, we initiated a
status review update and solicited
information from the public to help us
gather any additional information to
inform our review of Lolita’s
relationship to the Southern Resident
killer whale DPS. Based on the
information informing the 90-day
finding, the status review update, and
the public comments on the 90-day
finding, we published a proposed rule
on January 27, 2014 (79 FR 4313),
proposing to amend the regulatory
language of the ESA listing of the DPS
by removing the exclusion for captive
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members of the population and
requesting comments.
During the public comment period for
the proposed rule, which closed on
March 28, 2014, we received over
17,000 comments from citizens,
researchers, non-profit organizations,
and the public display industry;
comments came from the United States
and around the world. While we
solicited information concerning the
proposal to amend the regulatory
language describing the listing of the
Southern Resident killer whale DPS by
removing the exclusion of captive
whales and Lolita’s genetic heritage and
status, the vast majority of individual
commenters simply stated their support
for the proposal to include Lolita as a
member of the Southern Resident killer
whale DPS. Along with support for the
proposed rule or as a stand-alone
comment, many commenters suggested
that Lolita be freed from her captivity
and returned to her native waters of the
Pacific Northwest. Commenters also
expressed concern over Lolita’s current
care at the Miami Seaquarium under the
purview of the U.S. Department of
Agriculture’s Animal and Plant Health
Inspection Service (APHIS) under the
Animal Welfare Act (AWA). The AWA
captive care requirements are not under
NMFS jurisdiction and are beyond the
scope of our response to the petition;
thus, comments pertaining to AWA
compliance are not addressed in this
final rule.
In addition to a very large number of
brief comments in support of the
proposed rule, we received over 60
detailed comments raising substantive
issues. The majority of these comments
provided substantive support for
recognition of Lolita as a member of the
listed DPS. Several substantive
comments, primarily submitted by
groups or individuals associated with
the public display industry, opposed the
proposed rule, with several also
opposing any relocation of Lolita.
In addition to public review, we
solicited peer review of information
about Lolita’s heritage supporting our
conclusion in the proposed rule that
Lolita originated from the Southern
Resident killer whale population. On
July 1, 1994, the NMFS and USFWS
published a series of policies regarding
listings under the ESA, including a
policy for peer review of the scientific
data (59 FR 34270). The intent of the
peer review policy is to ensure that
listings are based on the best scientific
and commercial data available. Pursuant
to our 1994 policy on peer review, the
Data Quality Act, and the Office of
Management and Budget (OMB) Peer
Review Bulletin (OMB 2004), we
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solicited technical review from four
qualified specialists of specific
information regarding Lolita’s heritage
and our conclusion that she originated
from the Southern Resident killer whale
population as described in our status
review update (NMFS, 2013). A status
review of biological information and our
DPS determination was conducted by
the NMFS Northwest Fisheries Science
Center in response to the petition to
delist the Southern Resident killer
whale DPS and included a review of
information specific to Lolita’s genetic
heritage (NMFS, 2013). The peer review
request focused on the specific
paragraph regarding Lolita in the status
review update (NMFS, 2013) that
informed the proposed rule, and we
received reviews from two independent
experts. We received one comment on
the peer review plan and peer review
charge statement and provided that
comment letter to the peer reviewers.
We made the peer review charge,
comments received on the peer review
charge, and ultimate peer review report
available online at: https://
www.cio.noaa.gov/services_programs/
prplans/ID261.html. The peer reviewer
comments and conclusions and our
responses to public comments are
included in the summary below.
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Summary of Peer Review and Public
Comments Received
Below we summarize and address the
substantive public comments that were
received during the public comment
period for the proposed rule. In
addition, information from the peer
reviews is presented in both comment
summaries and responses. Substantive
comments and our responses are
organized by relevant topics.
Biological Information on Lolita’s Origin
Comment 1: Several commenters and
the two peer reviewers noted that the
best available scientific information
indicates that Lolita is most likely a
member of the Southern Resident
population. Many commenters cited the
acoustic and genetic evidence provided
in the proposed rule as proof that Lolita
is a member of the Southern Resident
community. Commenters cited the
references in the status review update,
including Hoelzel et al. (2007), Hoelzel
(personal communication), Ford (1987),
Candice Emmons (personal
communication), and Pilot et al. (2010)
(also referred to as Pilot (2009) in some
comments). Commenters cited Pilot et
al. (2010) as evidence that Lolita is
related to Southern Residents using one
genetic method, while others referenced
the same paper noting that three other
genetic methods did not indicate a
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relationship with Southern Residents.
One commenter addressed the sample
assigned to Lolita in Pilot et al. (2010),
referenced personal communications
with the lead author of the paper, and
noted that results from the tests are
insufficient to conclude that Lolita was
a Southern Resident killer whale. In
addition to the papers listed above, the
peer reviewers also provided additional
references to support their conclusions
that Lolita is most likely a member of
the Southern Resident population. One
peer reviewer noted that our summary
in the status review update (NMFS,
2013) was overly simplistic. The
comments on the peer review plan
focused on individual data points and
the uncertainties for individual genetic
tests and requested additional
information be provided to the peer
reviewers.
Response: We considered the best
available information regarding Lolita’s
origin, including genetic test results
from multiple papers, the peer reviews,
and other lines of evidence in making
our conclusions. In addition to the
original peer review request, we also
provided comments on the peer review
plan and additional information for the
reviewers to consider. The peer
reviewers stated that mitochondrial
DNA (mtDNA) tests are very likely
diagnostic of natal populations. The
mtDNA control region sequence is fixed
for a single haplotype within most killer
whale populations in the North Pacific.
Lolita has the haplotype for Southern
Residents, and the haplotype is distinct
from the haplotypes found in transient,
offshore and Northern Resident
communities (including SE Alaska and
Bering Sea). Based on sample sizes in
studies to date, it is extremely unlikely
that transient or Northern Residents
have a Southern Resident haplotype that
has gone undetected due to chance. Due
to smaller sample sizes for offshores, it
is harder to rule out that offshores might
contain the Southern Resident
haplotype in a small fraction of the
population (i.e., 10 percent), but it has
yet to be detected. The Southern
Resident haplotype is shared with
whales sampled off the Kamchatka
Peninsula in Russia and from Prince
William Sound in Alaska (BarrettLennard, 2000; Parsons et al., 2013);
however, additional data can be used to
rule out the possibility that Lolita
originated from these other populations.
Using microsatellite analysis,
researchers assigned Lolita to
populations using different programs
with varying probabilities and assessed
kinship (Hoelzel et al., 2007; Pilot et al.,
2010). In Pilot et al. (2010), Lolita was
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assigned to the Southern Resident
population with the highest probability
(0.464) and with low probability to
Kamchatka (0.016) or SE Alaska
residents (0.004). Tests for kinship using
microsatellite data found a presumed
match between Lolita and a member of
the Southern Resident L pod based on
one of four tests, but it was not a close
relationship (e.g., parent, offspring, or
full sibling). Lolita did not show
potential kinship with individuals of
any other population. Using a different
analysis, Pilot et al. (2010) also assigned
Lolita to a Southern Resident cluster
and not to the Kamchatka cluster. The
microsatellite data do not appear to
provide conclusive evidence on their
own to identify Lolita’s population of
origin, but the data support the finding
that she is a Southern Resident.
The peer reviews concluded that the
summary of our findings regarding
Lolita in our status review update
(NMFS, 2013) likely correctly
concluded that Lolita is a Southern
Resident and that, taken together, the
mtDNA and microsatellite DNA provide
a strong case for the assignment of Lolita
to the Southern Resident population.
While some comments focused on
individual test results to form
conclusions, we relied on all of the best
available information in the petition,
public comments on the 90-day finding
and the proposed rule, peer review, peer
reviewed journal articles, unpublished
science reports, and the recovery plan
(NMFS, 2008), taken together, to inform
our internal review and conclusions.
Based on the best available information
regarding the location of capture and
genetic information, we are confident
that Lolita originated from the Southern
Resident population.
Comment 2: One commenter provided
information from her study of the
specific acoustic call type produced by
Lolita, matching Lolita’s calls to
Southern Resident specific call types.
The commenter suggested that further
identification of Lolita’s calls could be
matched with specific matrilines. Other
commenters noted that there is no
statistically significant or peer reviewed
data or analysis that the calls recorded
opportunistically from Lolita match L
pod calls. In addition, commenters
noted that the Ford (1987) paper cited
in the status review did not include
specific information about Lolita and
her calls. One peer reviewer noted that
additional information about the timing
of the recording of Lolita’s calls and the
origin of the whale sharing Lolita’s tank
would shed light on whether Lolita was
an L pod whale or if she could have
learned L pod calls from another whale.
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Response: In the status review update
(NMFS, 2013), the Ford (1987) paper
was cited to demonstrate that calls can
be identified to population and also to
pod, and we acknowledge that it does
not include specific information about
Lolita’s calls. While the acoustic
information about Lolita’s calls is not
published in a peer reviewed article, the
personal communication by Candice
Emmons does lend an additional line of
evidence that is consistent with Lolita
originating from the Southern Resident
killer whale population. The study
provided by a commenter is also not a
peer reviewed published article. In
addition, the peer review comments also
raised uncertainty about identifying
Lolita by her acoustic calls based on the
personal communication. While we
considered the anecdotal and
unpublished information on Lolita’s
acoustic calls, noting the uncertainty
surrounding them, we relied on the
genetic data and capture location as the
primary support for Lolita’s status as a
member of the Southern Resident killer
whale population.
Comment 3: In addition to genetic and
acoustic information, Lolita’s capture
history was also mentioned by
commenters and peer reviewers as
evidence that she came from the
Southern Resident population. One
commenter noted photographs from the
capture operation were identified as
Southern Residents and that members of
different communities have never been
observed associating, concluding that all
of the whales captured at Penn Cove
were members of the Southern Resident
community. One commenter, however,
noted that the capture history raised
questions about Lolita’s origin,
mentioning that the total number of
whales in the area was too high to
account for only the Southern Residents
and that L pod whales were
photographed near the operation but not
in the net. The peer reviewers
referenced the sighting history of killer
whales in the capture area as support for
Lolita’s identification as a Southern
Resident.
Response: We did not receive any
photo-identification quality
photographs of the capture and have no
specific documentation of the captures
beyond the information summarized in
the Recovery Plan for Southern Resident
Killer Whales (NMFS, 2008) that
attributes captures from Penn Cove,
Washington, to the Southern Resident
population. One peer reviewer noted the
location of capture does not rule out
that she is a transient (but mtDNA
makes this highly unlikely), and that the
capture location makes it highly
unlikely that she is a Northern Resident,
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offshore, Western Pacific, Alaska
Resident or from a distant, poorly
known population. A review of the
information raised in public comments,
the peer reviews, comments on the peer
review plan, and other available
information finds this information
continues to find the capture
information regarding Lolita consistent
with her membership as a Southern
Resident. That review (Ford, 2014) notes
that based on what is known about the
ranges of North Pacific killer whales, the
Penn Cove, WA capture location limits
the possible populations of origin to
Southern Residents or transients which
are commonly seen, or far less likely to
Northern Residents (only seen a handful
of times in U.S. waters of the Salish Sea)
or offshores (only sighted six times in 30
years of observations and never south of
Admiralty Inlet) (Krahn et al., 2004;
Ford, 2006; Dahlheim et al., 2008).
Regular observations in the Salish Sea
have occurred since the mid-1970s,
several years after the capture in
question, and it seems highly unlikely
that the distributions and habits of these
populations would change dramatically
over that short period of time (Ford,
2014).
Comment 4: Several commenters
noted that, morphologically, Lolita’s
saddle patch patterns do not readily
match the majority of saddle patch
patterns of the Southern Resident DPS,
but they are more similar to saddle
patches of the Alaska and Bering Strait
residents. One peer reviewer suggested
saddle patch and dorsal fin shape could
be used to further address Lolita’s
origin.
Response: Bain (1988) found
differences between Northern and
Southern Resident saddle shapes and
Baird and Stacey (1988) reported
different distributions of saddle shapes
among residents and transients. Baird
and Stacey (1988) identified five
different patterns, with all five patterns
present in resident killer whales.
Lolita’s saddle shape appears to be
consistent with the ‘‘horizontal notch’’
type. While this saddle patch type is
seen in Alaska Residents, it is more
common in Southern Residents (Baird
and Stacey, 1988). The information
above regarding sighting records and the
capture location includes an assessment
by a peer reviewer, noting that it is
highly unlikely that Lolita is an Alaska
Resident.
Comment 5: Several commenters
reviewed the ESA section 4(a)(1) factors
and identified how they applied to
Lolita. Other commenters noted that
none of the threats identified in the
listing of the Southern Resident killer
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whale DPS (i.e., food scarcity, vessels,
contaminants) apply to Lolita.
Response: In March 2011, we
completed a 5-year review of the ESA
status of the Southern Resident killer
whale DPS, concluding that no change
was needed in its listing status and that
the Southern Resident killer whale DPS
would remain listed as endangered
(NMFS, 2011). The endangered status of
the DPS is not the subject of the
petitioned action. The petition requests
we include Lolita in the ESA listing of
Southern Residents and notes that an
analysis of the five ESA section 4(a)(1)
factors is not required to justify Lolita’s
inclusion in the DPS and that Lolita’s
genetic heritage is sufficient to support
her inclusion in the listing. We agree
that biological information regarding
Lolita’s origin and consideration of the
applicability of the ESA to captive
members of endangered species provide
a sufficient basis for our determination
and, therefore, do not include a review
of the section 4(a)(1) factors for Lolita or
the wild population in this notice.
Captivity and Release
Comment 6: One commenter
questioned why the ESA applied to
Lolita at all, considering she was held
in captivity prior to December 28, 1973,
and the date of the listing of the
Southern Resident killer whales.
Response: The commenter
presumably refers to section 9(b) of the
ESA, 16 U.S.C. 1538(b)(1), which
provides certain exemptions for animals
already held in captivity or a controlled
environment on either December 28,
1973, or the date of publication in the
Federal Register of the final regulation
adding such species to the list of
endangered species, provided that such
holding and any subsequent holding of
the animal is not in the course of a
commercial activity.
In fact, this section is not a blanket
exemption from the ESA for any animal
so held; rather, it only lifts the ban on
two very specific activities enumerated
in subsections (a)(1)(A) and (G) of
section 9: import or export of such
species, and violation of any regulation
pertaining to such species or to any
threatened species. In other words, all of
the other prohibitions of section 9 apply
to animals that were held in captivity
pre-ESA or pre-listing, including the
prohibitions on take as well as on
interstate or foreign commerce. Any
import or export of Lolita that might be
proposed in the future is beyond the
scope of this rulemaking. For additional
discussion of ESA section 9(b), see
American Society for the Prevention of
Cruelty to Animals v. Ringling Brothers
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and Barnum and Bailey Circus, 502
F.Supp. 2d 103 (2007).
Comment 7: Several commenters
noted that the ESA does not allow for
the exclusion of captive members from
a listed species based on their captive
status and referenced court cases (Safari
Club International v. Jewell and Alsea
Valley Alliance v. Evans, cited below in
response) and recent USFWS notices
regarding antelopes and chimpanzees
that were referenced in the proposed
rule. In addition, commenters noted that
if Lolita is included in the listing, the
ESA prohibitions on export, take, and
interstate commerce will apply to her.
Response: As the commenters note,
several courts have held, and NMFS
agrees, that the ESA does not allow for
captive held animals to be assigned
separate legal status from their wild
counterparts on the basis of their
captive status or through designation as
a separate DPS (Safari Club
International v. Jewell, 960 F.Supp. 2d
17 (D.D.C. 2013); Alsea Valley Alliance
v. Evans, 161 F. Supp. 2d 1154 (D.Or.
2001). As noted in this final rule, as
well as in recent regulations addressing
captive antelopes (78 FR 33790; June 5,
2013) and a proposed rule for
chimpanzees (78 FR 35201; June 12,
2013), captive members of a species
have the same legal status as the species
as a whole. Finally, as the commenters
note, captive members of a listed
species are also subject to the relevant
provisions of section 9 of the ESA as
warranted.
Comment 8: One commenter
expressed concern that including Lolita
in the ESA listing would result in a
violation of the Fifth Amendment,
denying the property owners their rights
without satisfying the Constitution’s
public use and just compensation
requirements. One commenter
supported their opposition to including
Lolita in the ESA listing by citing
examples of how extending regulations
to privately owned members of a listed
species could undermine private efforts
to avoid extinction and recover species
through private governance.
Commenters also noted that financial
considerations should not be considered
in listing decisions.
Response: First, section 4(b)(1)(A) of
the ESA and its legislative history
provides that listing decisions be based
‘‘solely’’ on the best scientific and
commercial data available without
reference to economic costs or private
party impacts (H.R. Rep. No. 97–567, at
12, 1982 U.S.C.C.A.N. 2807, 2812).
Second, to the extent there are concerns
about specific activities (including acts
supporting conservation) associated
with listed species, these issues are
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better evaluated in the context of a
specific permit request and through the
section 10 permit process, which
provides an avenue for defining,
evaluating, and authorizing specific
activities (50 CFR 222.301 et seq.).
Accordingly, speculating about whether
there are activities that property owners
may wish to take is beyond the scope of
this rule.
Comment 9: One commenter took
issue with our assertion that if Lolita
was included in the ESA listing, we
would not seek to amend critical habitat
to include consideration of her or her
captive environment. The commenter
cited the requirement to designate
critical habitat with the listing of a
species in section 4(a)(3)(A) of the ESA.
Response: NMFS designated critical
habitat for the Southern Resident killer
whale DPS on November 29, 2006 (71
FR 69054). NMFS interprets critical
habitat to comprise the habitat used by
the species in the wild, not the artificial
surroundings of a particular species
member in captivity, because those
areas do not include relevant primary
constituent elements of critical habitat
(70 FR 52630; September 2, 2005).
Accordingly, we do not intend to amend
the existing critical habitat designation
for Southern Resident killer whales with
respect to Lolita.
Comment 10: We received many
comments addressing the type and
scope of activities that might trigger
section 9 concerns and/or warrant
consideration for a section 10 permit.
These comments took varying positions
on the scope of activities that might fall
within the category of allowable captive
care activities.
Response: In the proposed rule, we
said that, depending on the
circumstances, we would likely not find
continued possession, care, and
maintenance of a captive animal to be
a violation of ESA section 9 (and
therefore, such activities would not
require a section 10 permit). Our
discussion in the proposed rule was
intended to be a general indication of
our views, not factual findings on
Lolita’s actual circumstances or any
proposals for future activities. Such
findings are beyond the scope of this
listing rule.
We appreciate the concerns raised by
the many comments regarding how the
ESA section 9 prohibitions might apply
to Lolita’s particular circumstances. We
believe these comments demonstrate the
need for a more focused evaluation of
these factors, which is more
appropriately performed as part of a
permit application process as opposed
to this listing rule. Should the Miami
Seaquarium apply for an ESA section 10
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7385
permit, the process would involve a
Federal Register notice of receipt
followed by a public comment period.
Comment 11: Commenters raised
questions about the Miami Seaquarium
conducting commercial activity with
Lolita, stating their belief that section
9(b) of the ESA allows for captives to
remain in captivity so long as they are
not held or used for purposes of
commercial activity. Other commenters
stated that there is nothing illegal about
exhibiting endangered animals for a fee.
Response: Some commenters may
have misinterpreted section 9(b) in this
regard. As noted above, section 9(b) is
a very limited exclusion from the
prohibition on import and export, as
well as certain regulatory requirements
not applicable here. Any future proposal
to import or export Lolita is beyond the
scope of this rule, and so we need not
further address the 9(b) exemption,
including its clause regarding
commercial activity, at this time.
Comment 12: One commenter urged
us to acknowledge that interstate
movement of Lolita or any other captive
listed species merely for display or as
part of an animal exhibition would not
require a permit under the ESA, citing
U.S.C. 1538(a)(E) and 50 CFR 17.3.
Response: At this time, the Miami
Seaquarium has not presented any
proposal to move Lolita, regardless of
purpose, so we will not address this
further in this listing rule, other than to
note that the cited CFR provision is a
regulation promulgated by the USFWS,
and is therefore applicable to species
under their jurisdiction.
Comment 13: Commenters expressed
concern over captivity of killer whales
in general and about Lolita’s current
care at the Miami Seaquarium under the
purview of APHIS under AWA. Other
commenters noted the high level of care
provided to Lolita at the Miami
Seaquarium.
Response: As noted above, Lolita’s
current captive care requirements are
regulated by APHIS under the AWA and
are currently the subject of ongoing
litigation (Animal Legal Defense Fund et
al. v. Elizabeth Goldentyer, USDA and
Marine Exhibition Corporation No. 14–
12260 (11th Circuit Court of Appeals
2014)). Specific AWA captive care
requirements are not under NMFS
jurisdiction and are beyond the scope of
our response to the petition. Therefore,
comments regarding AWA compliance
are not addressed in this final rule.
Comment 14: Many comments
supported Lolita’s transfer to a sea pen
or release from captivity into her home
waters. Some commenters, while in
favor of Lolita’s ultimate release, argued
that any decision on this issue in the
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absence of a specific proposal is
premature. Comments on whether there
would be any conservation benefit to
the conservation of wild killer whales
from Lolita’s release were mixed. Some
comments identified benefits to Lolita
and to the wild Southern Resident killer
whale population, such as her ability to
aid in the care of young whales (i.e.,
alloparenting). Others were against any
relocation efforts, claiming that there
would be no conservation benefits to
wild whales and noting Lolita currently
has a high level of care, contributes to
educating the public, and there are risks
to Lolita and the wild population
associated with transport and release.
One commenter noted that regulations
regarding marine mammal rehabilitation
under the MMPA declare that a marine
mammal that has been in human care
for 2 or more years is presumptively
non-releaseable.
Response: As noted above, the Miami
Seaquarium has not presented any
proposal to move (or release) Lolita. As
for any future proposal to release her,
we indicated in the proposed rule that
there were certain activities that we
believe could result in violations of
section 9 of the ESA, specifically
including ‘‘releasing a captive animal
into the wild.’’ 79 FR at 4318 (January
27, 2014). We based this on our
proposed rule listing five species of
sturgeon (since finalized at 79 FR 31222,
June 2, 2014). After taking into account
the numerous comments on this topic,
and examining our existing regulations,
policies and practices, we have decided
to elaborate on our views in this final
rule. Releasing captive marine mammals
to the wild is not without risk. Issues of
concern include: disease transmission
and/or unwanted genetic exchange
between released animals and wild
stocks; the ability of released animals to
adequately forage and defend
themselves from predators; and any
behavioral patterns developed in
captivity that could affect the social
behavior of wild animals, as well as the
social integration of the released
animals.
In fact, as one commenter noted,
NMFS’ MMPA regulations address a
presumption of non-releasability, as
well as dictate legal requirements under
the MMPA for any proposal to release
a captive animal. First, 50 CFR
216.27(a)(1)(iii), addressing stranded
marine mammals, states that the
animal’s potential for survival in the
wild must be evaluated at 6-month
intervals, ‘‘until 24 months from capture
or import, at which time there will be
a rebuttable presumption that release to
the wild is not feasible.’’ Second, 50
CFR 216.35(e) states: ‘‘Captive marine
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mammals shall not be released into the
wild unless specifically authorized by
the Office Director under a scientific
research or enhancement permit.’’
The issues surrounding any release of
Lolita to the wild are numerous and
complex and are not ripe for analysis in
this listing rule. Such issues would be
more appropriately evaluated in the
context of a specific section 10 permit
application. Any such process would
include rigorous review by the scientific
community, the Marine Mammal
Commission, and the public, and be
subject to an associated NEPA analysis,
prior to action being taken.
Changes From the Proposed Rule
There are no changes from the
proposed amendment to the ESA listing
of the Southern Resident killer whale
DPS in this final rule. This final rule
implements the amendment to the
listing language, removing the exclusion
for captive whales from the regulatory
description of the Southern Resident
killer whale DPS. The public comments
provided opposing positions on this
approach, as well as Lolita’s status as a
member of the Southern Resident killer
whale population. The peer reviews
supported Lolita’s status as a member of
the Southern Resident killer whale
population. See the Summary of Peer
Review and Public Comments Received
section above and the Final
Determination and Amendment to
Listing section below for information on
the additional data that support the
conclusion that captive members should
be included in the listing and the
determination that best available
science supports Lolita’s status as a
member of the Southern Resident killer
whale population and therefore the
ESA-listed DPS.
Determination of Taxon and DPS
Based on the best information
available, we previously concluded,
with advice from the 2004 BRT (Krahn
et al., 2004), that the Southern Resident
killer whale population (J, K, and L
pods) met the two criteria of the DPS
policy (discreteness and significance)
and constituted a DPS of the North
Pacific Resident subspecies. A detailed
analysis of (1) the reference taxon for
consideration under the DPS policy, (2)
the discreteness of the Southern
Resident population from other
populations within that taxon, and
(3) the significance of the Southern
Resident population to that taxon was
included in our 12-month determination
that the petition to delist was not
warranted (78 FR 47277; August 5,
2013) and is summarized below. Based
on our recent status review and in
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response to a petition to delist the
Southern Resident killer whale DPS, we
concluded that the best available
scientific information indicates that,
similar to our 2005 rulemaking when we
listed the Southern Resident DPS, the
North Pacific Resident subspecies is the
appropriate reference taxon for
considering whether the Southern
Resident killer whale population is
discrete and significant. In our 2005
rulemaking we concluded there was
strong evidence that the Southern
Resident killer whale population is
discrete from other North Pacific
Resident killer whale populations as
defined by the 1996 DPS policy. The
new information subsequent to 2004,
such as recent genetic studies, is
consistent with and generally
strengthens the conclusion that the
Southern Resident killer whale
population is a discrete population
within the North Pacific Resident taxon.
As in 2004, all the available information
clearly indicates that the Southern
Resident population is discrete from
other populations in the North Pacific
resident subspecies. In addition, we
concluded that the new information on
genetics and behavioral and cultural
diversity available since 2004 was
consistent with or strengthens the 2004
BRT’s conclusion that the Southern
Resident killer whale population meets
the significance criterion of the DPS
policy. In summary, in our 12-month
finding that delisting was not
warranted, we concluded that members
of the Southern Resident killer whale
population are discrete from other
populations within the North Pacific
Resident killer whale taxon and
significant with respect to the North
Pacific Resident killer whale taxon and
therefore comprise a valid DPS which
remains listed as endangered (78 FR
47277; August 5, 2013).
Final Determination and Amendment to
Listing
The petition maintains that Lolita is a
member of the Southern Resident killer
whale population and states that she
must, therefore, be included in the
listed DPS. As summarized above, our
consideration of the petitioned action
focuses on biological information
regarding Lolita’s genetic heritage and
the application of the ESA to captive
members of a listed species or DPS. The
petitioners contend that Lolita was
taken from L pod during captures on
August 8, 1970, in Penn Cove,
approximately 50 miles (80 km) north of
Seattle, Washington. The peer reviewers
referenced the capture location and
sighting history of different populations,
in addition to other information (i.e.,
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genetics), to support their conclusions
that Lolita most likely came from the
Southern Resident population. The
petition notes that Lolita’s mother is
believed to be L25, an adult female
Southern Resident killer whale who
remains in the wild, and that Lolita
makes the unique calls of the L25
subpod. In our recent status review
update (NMFS, 2013), we cited genetic
analysis completed since the original
2005 listing, that indicates Lolita has a
genotype consistent with a Southern
Resident origin (Hoelzel et al., 2007;
Hoelzel, personal communication), and
we noted that Lolita’s acoustic calls are
typical of L pod (Ford, 1987; Candice
Emmons, personal communication). The
status review update (NWFSC, 2013)
also cites information in Pilot et al.
(2010). As described above, in support
of the DPS determination for Southern
Resident killer whales, recent genetic
studies all indicate that the Southern
Resident population is significantly
differentiated and there is a high degree
of reproductive isolation from other
resident populations that comprise the
North Pacific Resident subspecies.
As described above in the response to
comments, the peer reviewers identified
that mtDNA tests are very likely
diagnostic of natal populations. The
mtDNA control region sequence is fixed
for a single haplotype within most killer
whale populations in the North Pacific.
Lolita has the haplotype for Southern
Residents, which is distinct from the
haplotypes found in transient, offshore,
and Northern Resident communities
(including SE Alaska and Bering Sea).
Based on sample sizes in studies to date,
it is extremely unlikely that transient or
Northern Residents have a Southern
Resident haplotype that has gone
undetected due to chance. Due to
smaller sample sizes for offshores, it is
harder to rule out that offshores might
contain the Southern Resident
haplotype in a small fraction of the
population (i.e., 10 percent), but it has
yet to be detected. The Southern
Resident haplotype is shared with
whales sampled off the Kamchatka
Peninsula in Russia and from Prince
William Sound in Alaska (BarrettLennard, 2000; Parsons et al., 2013), but
additional data can be used to rule out
the possibility that Lolita originated
from these other populations. Using
microsatellite analysis, researchers
assigned Lolita to population using
different programs with varying
probabilities and assessed kinship
(Hoelzel et al., 2007; Pilot et al., 2010).
In Pilot et al. (2010), Lolita was assigned
to the Southern Resident population
with the highest probability (0.464) and
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with low probability to Kamchatka
(0.016) or SE Alaska residents (0.004).
Tests for kinship found a putative match
between Lolita and a member of the
Southern Resident L pod based on one
of four tests, but it was not a close
relationship (e.g., parent, offspring, or
full sibling). Lolita did not show
potential kinship with individuals of
any other population. Using a different
analysis, Pilot et al. (2010) also assigned
Lolita to a Southern Resident cluster
and not to the Kamchatka cluster. The
microsatellite data do not appear to
provide conclusive evidence on their
own to identify Lolita’s population of
origin, but they are consistent with her
being a Southern Resident.
The peer review conclusions were
that our status review update (NMFS,
2013) was overly simplistic, but likely
correctly concluded that Lolita is a
Southern Resident and that, taken
together, the mtDNA and microsatellite
DNA data provide a strong case for the
assignment of Lolita to the Southern
Resident population. As described
above, we relied on information in the
petition, public comments on the 90-day
finding and the proposed rule, peer
review and best available information,
including peer reviewed journal articles
and unpublished science reports and
the recovery plan (NMFS, 2008) to
inform our internal review and
conclusions. Similar to the peer reviews
and as raised in public comments, we
acknowledge the uncertainty inherent in
individual test results and observations;
however, based on all of the best
available scientific information, taken
together, including results from
multiple genetic studies, as well as
other lines of evidence regarding
capture and sighting history, we can be
confident that Lolita originated from the
Southern Resident population (Ford,
2014). Differences in acoustic behavior
between populations of resident killer
whales also support the conclusion that
Southern Resident killer whales are
discrete and significant and, therefore,
qualify as a DPS. Ford (1987) describes
killer whale acoustic calls and how they
can be identified to population and even
to pod. While there is anecdotal
information that Lolita shares acoustic
characteristics with the members of the
Southern Resident killer whale DPS
found in the wild, this evidence is not
as strong as the genetic data. In
addition, morphological data, such as
saddle patch pattern, are also consistent
with, but not conclusive of, Lolita being
a Southern Resident. This best available
science supports Lolita’s status as a
member of the Southern Resident killer
whale population.
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7387
Some commenters contend that Lolita
not be included in the Southern
Resident killer whale DPS, similar to
other wild whales that are members of
the North Pacific Resident subspecies
(i.e., Northern Resident and Alaska
Resident killer whale populations).
These commenters fail to recognize the
previously discussed best available
science defining the genetic
characteristics that Lolita shares with
the Southern Resident killer whale DPS
and often highlighted individual test
results rather than all of the available
scientific information taken together.
We find the multiple genetic
characteristics constitute compelling
lines of evidence that render Lolita and
other members of the Southern Resident
killer whale DPS discrete from and
significant to the North Pacific Resident
subspecies (NMFS, 2013; Ford, 2014).
Additionally, while the ESA authorizes
the listing, delisting, or reclassification
of a species, subspecies, or DPS of a
vertebrate species, it does not authorize
the exclusion of the members of a subset
or portion of a listed species,
subspecies, or DPS from a listing
decision. In 2001, the U.S. District Court
in Eugene, Oregon (Alsea Valley
Alliance v. Evans, 161 F. Supp.2d 1154
(D. Or. 2001)) (Alsea), ruled that once
we had identified and listed a DPS (for
Oregon Coast coho), the ESA did not
allow listing only a subset (that which
excluded 10 captive hatchery stocks) of
that DPS. Accordingly, this case does
not authorize the exclusion of Lolita
from the Southern Resident Killer
Whale DPS listing based on the best
available science supporting her
membership in the DPS.
Other comments note that there are
other characteristics, such as behavior
and habitat use, that Lolita does not
share with the other wild members of
the Southern Resident killer whales and
suggest that NMFS could exercise its
discretion to identify a separate captive
only DPS. However, legislative history
surrounding the 1978 amendments to
the ESA that gave the Services the
authority to identify DPSs indicates that
Congress intended identification of
DPSs to be used for the identification of
wild populations, not separation of
captive held specimens from wild
members of the same taxonomic species
(see Endangered Species Act Oversight:
Hearing Before Senate Subcommittee on
Resource Protection, Senate Committee
on Environment and Public Works, 95th
Cong. 50 (July 7, 1977)). Additionally,
these arguments fail to adhere to
Congress’ directive to the Services that
the authority to designate DPSs be
exercised ‘‘sparingly’’ (Senate Report
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151, 96th Congress, 1st Session).
Finally, NMFS’ decision making
relevant to identifying a captive only
DPS, in this context, is discretionary
and not subject to judicial review (Safari
Club International v. Jewell, 960 F.
Supp. 2d 17 (DDC 2013)).
As described in the proposed rule (79
FR 4313; January 27, 2014), the ESA
does not support the exclusion of
captive members from a listing based
solely on their captive status. On its face
the ESA does not treat captives
differently. Rather, specific language in
section 9 and section 10 of the ESA
presumes their inclusion in the listed
entity, and captives are subject to
certain exemptions to section 9. Section
9(a)(1)(A)–(G) of the ESA applies to
endangered species regardless of their
captive status. However, section 9(b)
provides certain exemptions from the
9(a)(1)(A) and (a)(1)(G) prohibitions for
listed animals held in captivity or in a
controlled environment as of the date of
the species’ listing (or enactment of the
ESA), provided the holding in captivity
and any subsequent use is not in the
course of commercial activity.
Additionally, section 9(b)(2) refers to
captive raptors and identifies that the
prohibitions in 9(a)(1) shall not apply to
raptors legally held in captivity.
Section10(a)(1)(A) of the ESA allows
issuance of permits to ‘‘enhance the
propagation or survival’’ of the species.
This demonstrates that Congress
recognized the value of captive holding
and propagation of listed species held in
captivity but intended that such
specimens would be protected under
the ESA, with these activities generally
regulated by permit.
We have specifically identified
captive members as part of the listed
unit during listing actions, such as for
endangered smalltooth sawfish (68 FR
15674; April 1, 2003), and endangered
Atlantic sturgeon (77 FR 5914; February
6, 2012), and in the final listing of five
species of foreign sturgeon (79 FR
31222; June 2, 2014). Further, based
upon the purposes of the ESA and its
legislative history, courts have held and
the USFWS has recently concluded that
the ESA does not allow captive animals
to be assigned different legal status from
their wild counterparts on the basis of
their captive status (Safari Club
International v. Jewell, 960 F. Supp. 2d
17 (DDC 2013)). Subsequent to the
submission of the petition regarding
Lolita, USFWS published a proposed
rule to amend the listing status of
captive chimpanzees, so that all
chimpanzees (wild and captive) would
be listed as endangered (78 FR 35201;
June 12, 2013). USFWS also published
a 12-month finding that delisting the
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captive members of three listed antelope
species was not warranted (78 FR
33790; June 5, 2013).
In a recent notice announcing a Final
Policy of Interpretation of the Phrase
‘‘Significant Portion of Its Range (SPR)’’
in the Endangered Species Act’s
Definitions of ‘‘Endangered Species’’
and ‘‘Threatened Species’’ (79 FR
37578; July 1, 2014), the Services also
confirmed the legal status of captive
members of listed species. The notice
explains, with regard to species found
in captivity, the Services consider a
captive population to have no ‘‘range’’
separate from that of the species to
which it belongs (captive populations
cannot be considered a SPR). The notice
also states ‘‘captive members have the
same legal status as the species as a
whole.’’
Based on the preceding discussion,
the information submitted during the
public comment period, the peer
reviews, and best available science and
information, we find that captive
members of the Southern Resident killer
whale population should not be
excluded from the listed Southern
Resident killer whale DPS based on
their captive status. Accordingly, this
rule removes the exclusion for captive
whales in the regulatory language
describing the Southern Resident killer
whale DPS. Our finding is consistent
with the recent USFWS conclusions
regarding the status of captive animals
under the ESA and also with the Marine
Mammal Commission recommendation
to adopt a policy consistent with the
USFWS in the proposed chimpanzee
listing rule and treat all biological
members of the Southern Resident killer
whales as part of the DPS, regardless of
whether those individuals are in the
wild or in captivity (Marine Mammal
Commission letter, August 13, 2013).
As part of the 2005 ESA listing of the
Southern Resident killer whale DPS (70
FR 69903; November 18, 2005), we
conducted an analysis of the five ESA
section 4(a)(1) factors and concluded
that the DPS was in danger of extinction
and listed it as endangered. In March
2011, we completed a 5-year review of
the ESA status of the Southern Resident
killer whale DPS, concluding that no
change was needed in its listing status
and that the Southern Resident killer
whale DPS would remain listed as
endangered (NMFS, 2011). The petition
and several public comments included
an analysis of the five ESA section
4(a)(1) factors with respect to Lolita,
although petitioners note that the
analysis is not required to justify
Lolita’s inclusion in the DPS and that
Lolita’s genetic heritage is sufficient to
support her inclusion in the listing. We
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agree that biological information
regarding Lolita’s origin and
consideration of the applicability of the
ESA to captive members of endangered
species provide a sufficient basis for our
determination and, therefore, do not
include a review of the section 4(a)(1)
factors for Lolita or the wild population.
While progress toward recovery has
been achieved since the listing, as
described in the 5-year review, the
status of the DPS remains as
endangered. Since the 5-year review
was completed, additional actions have
been taken to address threats, such as
regulations to protect killer whales from
vessel impacts (76 FR 20870; April 14,
2011), completion of a scientific review
of the effects of salmon fisheries on
Southern Resident killer whales
(Hilborn, 2012), and ongoing technical
working groups with the Environmental
Protection Agency to assess
contaminant exposure. However, the
population growth outlined in the
biological recovery criteria and some of
the threats criteria have not been met.
We have no new information that would
change the recommendation in our 5year review that the Southern Resident
killer whale DPS remain classified as
endangered (NMFS, 2011). This final
rule amends the language describing the
Southern Resident killer whale DPS by
removing the exclusion of captive
whales. With this change, Lolita, a
female killer whale captured from the
Southern Resident killer whale
population in 1970, is not excluded
from the Southern Resident killer whale
DPS due to her captive status.
Effects of Amendment to Listing
Conservation measures provided for
species listed as endangered or
threatened under the ESA include
concurrent designation of critical
habitat if prudent and determinable (16
U.S.C. 1533(a)(3)(A)); recovery plans
and actions (16 U.S.C. 1536(f)); Federal
agency requirements to consult with
NMFS and to ensure its actions do not
jeopardize the species or result in
adverse modification or destruction of
critical habitat should it be designated
(16 U.S.C. 1536); and prohibitions on
taking (16 U.S.C. 1538). Following the
listing, we designated critical habitat
and completed a recovery plan for the
Southern Resident killer whale DPS. We
issued a final rule designating critical
habitat for the Southern Resident killer
whale DPS November 29, 2006 (71 FR
69055). The designation includes three
specific areas: (1) The Summer Core
Area in Haro Strait and waters around
the San Juan Islands; (2) Puget Sound;
and (3) the Strait of Juan de Fuca, which
together comprise approximately 2,560
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Federal Register / Vol. 80, No. 27 / Tuesday, February 10, 2015 / Rules and Regulations
square miles (6,630 square km). The
designation excludes areas with water
less than 20 feet (6.1 m) deep relative to
extreme high water. The designated
critical habitat will not be affected by
removing the exclusion of captive
whales from the regulatory language
describing the Southern Resident killer
whale DPS. As the USFWS identified in
its recent proposed chimpanzee rule,
there is an ‘‘anomaly of identifying the
physical and biological features that
would be essential to the conservation
of a species consisting entirely of
captive animals in an artificial
environment’’ (78 FR 35201; June 12,
2013). This observation also holds for a
listed entity with only one captive
member. In addition, the recent notice
announcing a final policy interpreting
Significant Portion of its Range under
the ESA notes the Services consider a
captive population to have no ‘‘range’’
separate from that of the species to
which it belongs (79 FR 37578; July 1,
2014). We do not intend to modify the
critical habitat designation to include
consideration of Lolita and her captive
environment.
After engaging stakeholders and
providing multiple drafts for public
comment, we announced the Final
Recovery Plan for the Southern Resident
killer whale DPS on January 24, 2008
(73 FR 4176). Lolita’s capture and
captivity is mentioned in the recovery
plan; however, the recovery actions in
the plan are focused on addressing the
threats to and the recovery of the wild
population. As the recovery plan is
updated in the future, we will consider
including an update that Lolita is
included in the DPS.
Sections 7(a)(2) of the ESA requires
Federal agencies to ensure that activities
they authorize, fund, or carry out are not
likely to jeopardize the continued
existence of a listed species, or to
adversely modify critical habitat. In the
USFWS proposed rule for chimpanzees
(78 FR 35201; June 12, 2013), USFWS
identifies that ‘‘the section 7
consultation process is not well suited
to analysis of adverse impacts posed to
a purely captive-held group of
specimens given that such specimens
are maintained under controlled,
artificial conditions.’’ This observation
also holds for a listed entity with only
one captive member. Previous guidance
on examples of Federal actions that
have the potential to impact Southern
Resident killer whales was focused on
activities that may affect wild whales.
Additional considerations of actions
that have the potential to affect
Southern Resident killer whales,
including Lolita, will be considered
along with prohibitions on activities
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15:13 Feb 09, 2015
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that affect the Southern Resident killer
whale DPS. Some of these
considerations are discussed below.
Take Prohibitions and Identification of
Those Activities That Might Constitute
a Violation of Section 9 of the ESA
On July 1, 1994, NMFS and USFWS
published a policy (59 FR 34272) that
requires us to identify, to the maximum
extent practicable at the time a species
is listed, those activities that would or
would not constitute a violation of
section 9 of the ESA. The ESA does not
prohibit possession of animals lawfully
taken into captivity, so a permit is
required only if the person possessing
the animal intends to engage in an
otherwise prohibited act. Prohibited
activities for ESA-listed endangered
species include, but are not limited to:
(1) ‘‘take’’ of such species, as defined in
the ESA (including to harass, harm,
pursue, hunt, shoot, wound, kill, trap,
capture, or collect, or attempt to engage
in any such conduct); (2) delivering,
receiving, carrying, transporting, or
shipping in interstate or foreign
commerce, in the course of a
commercial activity, any such species;
or (3) selling or offering for sale in
interstate or foreign commerce any such
species.
In the proposed rule, we said that,
depending on the circumstances, we
would not likely find continued
possession, care, and maintenance of a
captive animal to be a violation of
section 9 (and that therefore, such
activities would not require a section 10
permit). As noted above, we received
numerous comments addressing the
types of activities that might trigger
section 9 concerns and/or warrant
consideration for a section 10 permit.
We believe these comments demonstrate
the need for a more focused evaluation
of these factors, which is more
appropriately performed as part of a
permit application process as opposed
to this listing rule.
Likewise, we indicated in the
proposed rule certain activities that we
believe could result in violations of
section 9 of the ESA, specifically
including ‘‘releasing a captive animal
into the wild.’’ 79 FR at 4318 (January
27, 2014). We based this on our
proposed rule listing five species of
sturgeon (since finalized at 79 FR 31222,
June 2, 2014).
In this final rule, NMFS notes that
issues surrounding any release of Lolita
to the wild are numerous and complex
and are not ripe for analysis in this
listing rule. Such issues would be better
evaluated in the context of a specific
section 10 permit application. Any such
process would include rigorous review
PO 00000
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Fmt 4700
Sfmt 4700
7389
by the scientific community, the Marine
Mammal Commission, and the public,
and be subject to an associated NEPA
analysis, prior to action being taken.
References Cited
The complete citations for the
references used in this document can be
obtained by contacting NMFS (See
ADDRESSES and FOR FURTHER
INFORMATION CONTACT) or on our Web
page at: https://
www.westcoast.fisheries.noaa.gov/
protected_species/marine_mammals/
killer_whale/lolita_petition.html.
Information Quality Act and Peer
Review
In December 2004, the Office of
Management and Budget (OMB) issued
a Final Information Quality Bulletin for
Peer Review establishing minimum peer
review standards, a transparent process
for public disclosure of peer review
planning, and opportunities for public
participation. The OMB Bulletin,
implemented under the Information
Quality Act (Public Law 106–554), is
intended to enhance the quality and
credibility of the Federal government’s
scientific information, and applies to
influential or highly influential
scientific information disseminated on
or after June 16, 2005. To satisfy our
requirements under the OMB Bulletin,
we obtained independent peer review of
the information on Lolita in our status
review update (NMFS, 2013). Four
independent specialists were selected
from the academic and scientific
community, Federal and state agencies,
and the private sector for this review
(with two respondents). All peer
reviewer comments were addressed in
this final rule. The peer review process
is detailed at: https://www.cio.noaa.gov/
services_programs/prplans/ID261.html.
Classification
National Environmental Policy Act
(NEPA)
The 1982 amendments to the ESA, in
section 4(b)(1)(A), restrict the
information that may be considered
when assessing species for listing. Based
on this limitation of criteria for a listing
decision and the opinion in Pacific
Legal Foundation v. Andrus, 657 F. 2d
829 (6th Cir. 1981), we have concluded
that NEPA does not apply to ESA listing
actions. (See NOAA Administrative
Order 216–6.)
Executive Order 12866, Regulatory
Flexibility Act, and Paperwork
Reduction Act
As noted in the Conference Report on
the 1982 amendments to the ESA,
economic impacts cannot be considered
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when assessing the status of a species.
Therefore, the economic analysis
requirements of the Regulatory
Flexibility Act are not applicable to the
listing process. In addition, this final
rule is exempt from review under
Executive Order 12866. This final rule
does not contain a collection-ofinformation requirement for the
purposes of the Paperwork Reduction
Act.
provide continuing and meaningful
dialogue on issues of mutual state and
Federal interest, this final rule will be
shared with the relevant state agencies
in each state in which the species is
believed to occur.
Executive Order 13122, Federalism
Dated: February 4, 2015.
Eileen Sobeck,
Assistant Administrator for Fisheries,
National Marine Fisheries Service.
In accordance with E.O. 13132, we
determined that this final rule does not
have significant federalism effects and
that a federalism assessment is not
required. In keeping with the intent of
the Administration and Congress to
List of Subjects in 50 CFR Part 224
Administrative practice and
procedure, Endangered and threatened
species, Reporting and recordkeeping
requirements.
Common name
Scientific name
Description of listed entity
1. The authority citation for part 224
continues to read as follows:
■
Authority: 16 U.S.C. 1531–1543 and 16
U.S.C. 1361 et seq.
2. In § 224.101, in the table in
paragraph (h), revise the entry for
‘‘Whale, killer (Southern Resident
DPS)’’ to read as follows:
■
§ 224.101 Enumeration of endangered
marine and anadromous species.
*
For the reasons set out in the
preamble, 50 CFR part 224 is amended
as follows:
Species1
PART 224—ENDANGERED MARINE
AND ANADROMOUS SPECIES
*
*
(h) * * *
*
*
Citation(s) for listing
determination(s)
Critical
habitat
ESA Rules
*
*
[Insert citation] 2/10/2015
226.206
*
224.103
Marine Mammals
*
Whale, killer (Southern
Resident DPS).
*
*
Orcinus orca .....................
*
*
*
Killer whales from the J, K,
and L pods.
*
*
*
*
*
1 Species
includes taxonomic species, subspecies, distinct population segments (DPSs) (for a policy statement, see 61 FR 4722, February 7,
1996), and evolutionarily significant units (ESUs) (for a policy statement, see 56 FR 58612, November 20, 1991).
*
*
*
*
*
[FR Doc. 2015–02604 Filed 2–9–15; 8:45 am]
BILLING CODE 3510–22–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 660
[Docket No. 131119977–4381–02]
RIN 0648–XD640
Magnuson-Stevens Act Provisions;
Fisheries Off West Coast States;
Pacific Coast Groundfish Fishery;
Pacific Whiting Allocations and
Fishery Closure; Pacific Whiting
Seasons
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Reapportionment of tribal
Pacific whiting allocation, and
implementation of an Ocean Salmon
Conservation Zone to protect Chinook
salmon.
rljohnson on DSK3VPTVN1PROD with RULES
AGENCY:
This document announces the
reapportionment of 45,000 metric tons
SUMMARY:
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15:13 Feb 09, 2015
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(mt) of Pacific whiting from the tribal
allocation to the non-tribal commercial
fishery sectors via two actions, in order
to allow full utilization of the Pacific
whiting resource. It also announces the
implementation of an Ocean Salmon
Conservation Zone that prohibited the
targeting of Pacific whiting with
midwater trawl gear shoreward of
approximately 100 fathoms (fm) (183 m)
to reduce Chinook salmon bycatch in
the Pacific whiting fishery.
DATES: The rules set out in this
document were made through automatic
action, and are published in the Federal
Register as soon as practicable after they
are issued. The Ocean Salmon
Conservation Zone was effective 0800
local time October 20, 2014 until
December 31, 2014. The
reapportionments of Pacific whiting
were effective from 1200 local time,
September 12, 2014 (25,000 mt) and
2000 local time October 23, 2014
(additional 20,000 mt), until December
31, 2014. Comments will be accepted
through February 25, 2015.
ADDRESSES: You may submit comments,
identified by NOAA–NMFS–2014–0020
by any of the following methods:
• Electronic Submissions: Submit all
electronic public comments via the
Federal eRulemaking Portal at
PO 00000
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www.regulations.gov/
#!docketDetail;D=NOAA-NMFS-20140020, click the ‘‘Comment Now!’’ icon,
complete the required fields, and enter
or attach your comments.
• Mail: William W. Stelle, Jr.,
Regional Administrator, West Coast
Region, NMFS, 7600 Sand Point Way
NE., Seattle, WA 98115–0070, Attn:
Miako Ushio.
Instructions: Comments sent by any
other method, to any other address or
individual, or received after the end of
the comment period, may not be
considered by NMFS. All comments
received are a part of the public record.
All personal identifying information
(e.g., name, address, etc.), confidential
business information, or otherwise
sensitive information submitted
voluntarily by the sender will be
publicly accessible. NMFS will accept
anonymous comments (enter ‘‘N/A’’ in
the required fields if you wish to remain
anonymous).
FOR FURTHER INFORMATION CONTACT:
Miako Ushio (West Coast Region,
NMFS), phone: 206–526–4644 or email:
miako.ushio@noaa.gov.
SUPPLEMENTARY INFORMATION:
E:\FR\FM\10FER1.SGM
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Agencies
[Federal Register Volume 80, Number 27 (Tuesday, February 10, 2015)]
[Rules and Regulations]
[Pages 7380-7390]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2015-02604]
=======================================================================
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 224
[Docket No. 130321272-5109-03]
RIN 0648-XC589
Listing Endangered or Threatened Species: Amendment to the
Endangered Species Act Listing of the Southern Resident Killer Whale
Distinct Population Segment
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: On January 25, 2013, we, NMFS, received a petition submitted
by the People for the Ethical Treatment of Animals Foundation to remove
the exclusion of captive animals from the endangered species listing of
Southern Resident killer whale DPS, as well as, recognize the captive
killer whale (Orcinus orca) ``Lolita'' as a protected member of the
endangered Southern Resident killer whale Distinct Population Segment
(DPS). We completed a status review and published a proposed rule, and
we are now amending the regulatory language of the Endangered Species
Act (ESA) listing of the DPS by removing the exclusion for captive
members of the population. We have further determined that Lolita, a
female killer whale captured from the Southern Resident killer whale
population in 1970 who resides at the Miami Seaquarium in Miami,
Florida, is not excluded from the Southern Resident killer whale DPS
due to her captive status.
We proposed to amend the regulatory language of the ESA listing to
remove the exclusion for captive whales from the Southern Resident
killer whale DPS on January 27, 2014. Additionally, we solicited
scientific and commercial information pertaining to the proposed rule
and also conducted a peer review of the status review information on
Lolita that informed the proposed rule. We have determined that captive
members of the Southern Resident killer whale population should be
included in the listed Southern Resident killer whale DPS. This rule
amends the regulatory language of the listing to remove the exclusion
for captive members of the DPS.
DATES: This final rule becomes effective on May 11, 2015.
ADDRESSES: Information supporting this final rule can be found on our
Web site at: https://www.westcoast.fisheries.noaa.gov/protected_species/marine_mammals/killer_whale/lolita_petition.html.
Or in our office at:
Protected Resources Division, NMFS, Northwest Region,
Protected Resources Division, 7600 Sand Point Way NE., Attention Lynne
Barre, Branch Chief.
FOR FURTHER INFORMATION CONTACT: Lynne Barre, NMFS Northwest Region,
(206) 526-4745; Marta Nammack, NMFS Office of Protected Resources,
(301) 427-8469.
SUPPLEMENTARY INFORMATION:
ESA Statutory Provisions and Policy Considerations
On January 25, 2013, we received a petition submitted by the People
for the Ethical Treatment of Animals Foundation on behalf of the Animal
Legal Defense Fund, Orca Network, Howard Garrett, Shelby Proie, Karen
Munro, and Patricia Sykes to remove the exclusion of captive whales
from the SRKW DPS ESA listing and to include the killer whale known as
Lolita in the ESA listing of the Southern Resident killer whales.
Lolita is a female killer whale captured from the Southern Resident
population in 1970, who currently resides at the Miami Seaquarium in
Miami, Florida. Copies of the petition are available upon request (see
ADDRESSES, above).
In accordance with section 4(b)(3)(A) of the ESA, to the maximum
extent practicable within 90 days of receipt of a petition to list,
reclassify, or delist a species, the Secretary of Commerce is required
to make a finding on whether that petition presents substantial
scientific or commercial information indicating that the petitioned
action may be warranted, and to promptly publish such finding in the
Federal Register (16 U.S.C. 1533(b)(3)(A)). The Secretary of Commerce
has delegated this duty to NMFS. If we find that the petition presents
substantial information indicating that the petitioned action may be
warranted, we must commence a review of the status of the species
concerned, during which we will conduct a comprehensive review of the
best available scientific and commercial information. On April 29, 2013
we made a finding (78 FR 25044) that there was sufficient information
indicating that the petitioned action may be warranted and requested
comments to inform a status review.
After accepting a petition and initiating a status review, within
12 months of receipt of the petition we must conclude the review with a
determination that the petitioned action is not warranted, or a
proposed determination that the action is warranted. Under specific
facts, we may also issue a determination that the action is warranted
but precluded. On January 27, 2014 we made a finding (79 FR 4313) that
the petitioned action to remove the exclusion of captive killer whales
from the ESA listing of the Southern Resident killer whale DPS and to
include captive killer whales in the ESA listing of the Southern
Resident killer whale DPS was warranted and proposed to amend the
regulatory language describing the DPS by removing the current
exclusion for captive whales. Within 12 months of issuing a proposed
rule on a listing determination, we must publish a final regulation to
implement the determination or publish a notice extending the 12-month
period. This notice is a final rule to implement our
[[Page 7381]]
determination that the petitioned action is warranted and to amend the
language describing the endangered listing of the Southern Resident
killer whale DPS by removing the exclusion for captive whales.
Under the ESA, the term ``species'' means a species, a subspecies,
or a DPS of a vertebrate species (16 U.S.C. 1532(16)). A joint NMFS-
U.S. Fish and Wildlife (USFWS) policy clarifies the Services'
interpretation of the phrase ``Distinct Population Segment,'' or DPS
(61 FR 4722; February 7, 1996). The DPS Policy requires the
consideration of two elements when evaluating whether a vertebrate
population segment qualifies as a DPS under the ESA: (1) Discreteness
of the population segment in relation to the remainder of the species/
taxon, and, if discrete; (2) the significance of the population segment
to the species/taxon.
A species is ``endangered'' if it is in danger of extinction
throughout all or a significant portion of its range, and
``threatened'' if it is likely to become endangered within the
foreseeable future throughout all or a significant portion of its range
(ESA sections 3(6) and 3(20), respectively, 16 U.S.C. 1532(6) and
(20)). Thus, we interpret an ``endangered species'' to be one that is
presently in danger of extinction. A ``threatened species,'' on the
other hand, is not presently in danger of extinction, but is likely to
become so in the foreseeable future (that is, at a later time). In
other words, the primary statutory difference between a threatened
species and an endangered species is the timing of when a species may
be in danger of extinction, either presently (endangered) or in the
foreseeable future (threatened). Pursuant to the ESA and our
implementing regulations, we determine whether a species is threatened
or endangered based on any one or a combination of the following
section 4(a)(1) factors: the present or threatened destruction,
modification, or curtailment of habitat or range; overutilization for
commercial, recreational, scientific, or educational purposes; disease
or predation; inadequacy of existing regulatory mechanisms; and any
other natural or manmade factors affecting the species' existence (16
U.S.C. 1533(a)(1), 50 CFR 424.11(c)).
We make listing determinations based on the best available
scientific and commercial data available after conducting a review of
the status of the species and after taking into account efforts being
made by any State or foreign nation or political subdivision thereof to
protect the species.
Background
Three distinct forms or ecotypes of killer whales, termed
residents, transients, and offshores, are recognized in the
northeastern Pacific Ocean. Resident killer whales in U.S. waters are
distributed from Alaska to California, with four distinct populations:
Southern, Northern, Southern Alaska, and Western Alaska (Krahn et al.,
2002; 2004). Resident killer whales are fish eaters and live in stable
matrilineal pods. The West Coast transient killer whales have a
different social structure, are found in smaller groups, and eat marine
mammals. Offshore killer whales are found in large groups, and their
diet is presumed to consist primarily of fish, including sharks. While
the ranges of the different ecotypes of whales overlap in the
northeastern Pacific Ocean, available genetic data indicate that there
is a high degree of reproductive isolation among residents, transients,
and offshores (Krahn et al., 2004; NMFS, 2013).
The Southern Resident killer whale population consists of three
pods, identified as J, K, and L pods, that reside for part of the year
in the inland waterways of Washington State and British Columbia
(Strait of Georgia, Strait of Juan de Fuca, and Puget Sound),
principally during the late spring, summer, and fall (NMFS, 2008). Pods
visit coastal sites off Washington and Vancouver Island, and travel as
far south as central California and as far north as Southeast Alaska
(Ford et al., 2000; NMFS, 2008; Department of Fisheries and Oceans,
unpublished data).
In 2001 we received a petition to list the Southern Resident killer
whale population as threatened or endangered under the ESA (CBD, 2001)
and we formed a Biological Review Team (BRT) to assist with a status
review (NMFS, 2002). After conducting the status review, we determined
that listing the Southern Resident killer whale population as a
threatened or endangered species was not warranted because the science
at that time did not support identifying the Southern Resident killer
whale population as a DPS as defined by the ESA (67 FR 44133; July 1,
2002). Because of the uncertainties regarding killer whale taxonomy
(i.e., whether killer whales globally should be considered as one
species or as multiple species and/or subspecies), we announced that we
would reconsider the taxonomy of killer whales within 4 years.
Following the determination, the Center for Biological Diversity and
other plaintiffs challenged our ``not warranted'' finding under the ESA
in U.S. District Court. The U.S. District Court for the Western
District of Washington issued an order on December 17, 2003, which set
aside our ``not warranted'' finding and remanded the matter to us for
redetermination of whether the Southern Resident killer whale
population should be listed under the ESA (Center for Biological
Diversity v. Lohn, 296 F. Supp. 2d. 1223 (W.D. Wash. 2003)). The court
found that where there is ``compelling evidence that the global Orcinus
orca taxon is inaccurate,'' the agency may not rely on ``a lack of
consensus in the field of taxonomy regarding the precise, formal
taxonomic redefinition of killer whales.'' As a result of the court's
order, we co-sponsored a Cetacean Taxonomy workshop in 2004, which
included a special session on killer whales, and reconvened a BRT to
prepare an updated status review document for Southern Resident killer
whales (NMFS, 2004).
The BRT agreed that the Southern Resident killer whale population
likely belongs to an unnamed subspecies of resident killer whales in
the North Pacific, which includes the Southern and Northern Residents,
as well as the resident killer whales of Southeast Alaska, Prince
William Sound, Kodiak Island, the Bering Sea and Russia (but not
transients or offshores). The BRT concluded that the Southern Resident
killer whale population is discrete from other populations within the
North Pacific Resident taxon and significant with respect to the North
Pacific Resident taxon and therefore should be considered a DPS. In
addition, the BRT conducted a population viability analysis, which
modeled the probability of species extinction under a range of
assumptions. Based on the findings of the status review and an
evaluation of the factors affecting the DPS, we published a proposed
rule to list the Southern Resident killer whale DPS as threatened on
December 22, 2004 (69 FR 76673). After considering public comments on
the proposed rule and other available information, we reconsidered the
status of the Southern Resident killer whale DPS and issued a final
rule to list the Southern Resident killer whale DPS as endangered on
November 18, 2005 (70 FR 69903). The regulatory language in the listing
limited the DPS to whales from J, K and L pods, wherever they are found
in the wild, and not including Southern Resident killer whales placed
in captivity prior to listing or their captive born progeny.
Following the listing, we designated critical habitat, completed a
recovery plan, and conducted a 5-year review for
[[Page 7382]]
the Southern Resident killer whale DPS. We issued a final rule
designating critical habitat for the Southern Resident killer whale DPS
on November 29, 2006 (71 FR 69055). After engaging stakeholders and
providing multiple drafts for public comment, we announced the Final
Recovery Plan for the Southern Resident killer whale DPS on January 24,
2008 (73 FR 4176). We have continued working with partners to implement
actions in the recovery plan. In March 2011, we completed a 5-year
review of the ESA status of the Southern Resident killer whale DPS,
concluding that no change was needed in its listing status and that the
Southern Resident killer whale DPS would remain listed as endangered
(NMFS, 2011). The 5-year review also noted that there was no relevant
new information for this species regarding the application of the DPS
policy.
On August 2, 2012, we received a petition submitted by the Pacific
Legal Foundation on behalf of the Center for Environmental Science
Accuracy and Reliability, Empresas Del Bosque, and Coburn Ranch to
delist the endangered Southern Resident killer whale DPS under the ESA.
We made a 90-day finding accepting the petition and soliciting
information to inform a status review (77 FR 70733; November 27, 2012).
Based on a review of the scientific information (NWFSC, 2013) and our
full status review, we issued a 12-month finding on August 5, 2013,
that the petitioned action was not warranted and the Southern Resident
killer whale DPS remains listed as endangered (78 FR 47277).
Lolita Petition
On January 25, 2013, we received a petition submitted by the People
for the Ethical Treatment of Animals Foundation on behalf of the Animal
Legal Defense Fund, Orca Network, Howard Garrett, Shelby Proie, Karen
Munro, and Patricia Sykes to remove the exclusion of captive killer
whales from the ESA listing of the Southern Resident Killer Whale DPS
and to include the killer whale known as Lolita in the ESA listing of
the Southern Resident killer whales. The petition described Lolita, a
female killer whale captured from the Southern Resident population in
1970, who currently resides at the Miami Seaquarium in Miami, Florida,
as the only remaining member of the Southern Residents alive in
captivity. The petitioners presented information about Lolita's origin
and contended that Lolita is a member of the endangered Southern
Resident DPS and should be included within the ESA listing. In
addition, they provided a legal argument that ``the ESA applies to
captive members of listed species'' and asserted that ``NMFS has a non-
discretionary duty to include Lolita in the listing of the Southern
Resident killer whales under the ESA.'' The petition also included
information about how each of the five section 4(a)(1) factors applies
with respect to Lolita. Lastly, the petitioners contended that
including Lolita in the ESA listing will contribute to conservation of
the wild Southern Resident killer whale population.
On April 29, 2013, we found that the information contained in the
petition, viewed in the context of information readily available in our
files, presented substantial scientific information that would lead a
reasonable person to believe the petitioned action may be warranted (78
FR 25044). We noted that the information on Lolita's genetic heritage
and consideration of captive individuals under the ESA provided a basis
for us to accept the petition. The petition included an assessment of
how listing Lolita would help conserve the wild Southern Resident
population and also a review of the 4(a)(1) factors described earlier
and considered in listing determinations. Our 90-day finding accepting
the petition, however, was based on the biological information
regarding Lolita's genetic heritage and consideration of the
applicability of the ESA to captive members of endangered species. Our
review of Lolita's status with respect to the Southern Resident killer
whale DPS similarly focused on these two aspects and did not include a
review of the Section 4(a)(1) factors for Lolita or the wild
population. Our status review considered the best available information
including information received through the public comment period, a
review of scientific information conducted by our Northwest Fisheries
Science Center, including published peer-reviewed journal articles and
unpublished scientific reports, and information in the petition.
Upon publishing our 90-day finding accepting the petition, we
initiated a status review update and solicited information from the
public to help us gather any additional information to inform our
review of Lolita's relationship to the Southern Resident killer whale
DPS. Based on the information informing the 90-day finding, the status
review update, and the public comments on the 90-day finding, we
published a proposed rule on January 27, 2014 (79 FR 4313), proposing
to amend the regulatory language of the ESA listing of the DPS by
removing the exclusion for captive members of the population and
requesting comments.
During the public comment period for the proposed rule, which
closed on March 28, 2014, we received over 17,000 comments from
citizens, researchers, non-profit organizations, and the public display
industry; comments came from the United States and around the world.
While we solicited information concerning the proposal to amend the
regulatory language describing the listing of the Southern Resident
killer whale DPS by removing the exclusion of captive whales and
Lolita's genetic heritage and status, the vast majority of individual
commenters simply stated their support for the proposal to include
Lolita as a member of the Southern Resident killer whale DPS. Along
with support for the proposed rule or as a stand-alone comment, many
commenters suggested that Lolita be freed from her captivity and
returned to her native waters of the Pacific Northwest. Commenters also
expressed concern over Lolita's current care at the Miami Seaquarium
under the purview of the U.S. Department of Agriculture's Animal and
Plant Health Inspection Service (APHIS) under the Animal Welfare Act
(AWA). The AWA captive care requirements are not under NMFS
jurisdiction and are beyond the scope of our response to the petition;
thus, comments pertaining to AWA compliance are not addressed in this
final rule.
In addition to a very large number of brief comments in support of
the proposed rule, we received over 60 detailed comments raising
substantive issues. The majority of these comments provided substantive
support for recognition of Lolita as a member of the listed DPS.
Several substantive comments, primarily submitted by groups or
individuals associated with the public display industry, opposed the
proposed rule, with several also opposing any relocation of Lolita.
In addition to public review, we solicited peer review of
information about Lolita's heritage supporting our conclusion in the
proposed rule that Lolita originated from the Southern Resident killer
whale population. On July 1, 1994, the NMFS and USFWS published a
series of policies regarding listings under the ESA, including a policy
for peer review of the scientific data (59 FR 34270). The intent of the
peer review policy is to ensure that listings are based on the best
scientific and commercial data available. Pursuant to our 1994 policy
on peer review, the Data Quality Act, and the Office of Management and
Budget (OMB) Peer Review Bulletin (OMB 2004), we
[[Page 7383]]
solicited technical review from four qualified specialists of specific
information regarding Lolita's heritage and our conclusion that she
originated from the Southern Resident killer whale population as
described in our status review update (NMFS, 2013). A status review of
biological information and our DPS determination was conducted by the
NMFS Northwest Fisheries Science Center in response to the petition to
delist the Southern Resident killer whale DPS and included a review of
information specific to Lolita's genetic heritage (NMFS, 2013). The
peer review request focused on the specific paragraph regarding Lolita
in the status review update (NMFS, 2013) that informed the proposed
rule, and we received reviews from two independent experts. We received
one comment on the peer review plan and peer review charge statement
and provided that comment letter to the peer reviewers. We made the
peer review charge, comments received on the peer review charge, and
ultimate peer review report available online at: https://www.cio.noaa.gov/services_programs/prplans/ID261.html. The peer
reviewer comments and conclusions and our responses to public comments
are included in the summary below.
Summary of Peer Review and Public Comments Received
Below we summarize and address the substantive public comments that
were received during the public comment period for the proposed rule.
In addition, information from the peer reviews is presented in both
comment summaries and responses. Substantive comments and our responses
are organized by relevant topics.
Biological Information on Lolita's Origin
Comment 1: Several commenters and the two peer reviewers noted that
the best available scientific information indicates that Lolita is most
likely a member of the Southern Resident population. Many commenters
cited the acoustic and genetic evidence provided in the proposed rule
as proof that Lolita is a member of the Southern Resident community.
Commenters cited the references in the status review update, including
Hoelzel et al. (2007), Hoelzel (personal communication), Ford (1987),
Candice Emmons (personal communication), and Pilot et al. (2010) (also
referred to as Pilot (2009) in some comments). Commenters cited Pilot
et al. (2010) as evidence that Lolita is related to Southern Residents
using one genetic method, while others referenced the same paper noting
that three other genetic methods did not indicate a relationship with
Southern Residents. One commenter addressed the sample assigned to
Lolita in Pilot et al. (2010), referenced personal communications with
the lead author of the paper, and noted that results from the tests are
insufficient to conclude that Lolita was a Southern Resident killer
whale. In addition to the papers listed above, the peer reviewers also
provided additional references to support their conclusions that Lolita
is most likely a member of the Southern Resident population. One peer
reviewer noted that our summary in the status review update (NMFS,
2013) was overly simplistic. The comments on the peer review plan
focused on individual data points and the uncertainties for individual
genetic tests and requested additional information be provided to the
peer reviewers.
Response: We considered the best available information regarding
Lolita's origin, including genetic test results from multiple papers,
the peer reviews, and other lines of evidence in making our
conclusions. In addition to the original peer review request, we also
provided comments on the peer review plan and additional information
for the reviewers to consider. The peer reviewers stated that
mitochondrial DNA (mtDNA) tests are very likely diagnostic of natal
populations. The mtDNA control region sequence is fixed for a single
haplotype within most killer whale populations in the North Pacific.
Lolita has the haplotype for Southern Residents, and the haplotype is
distinct from the haplotypes found in transient, offshore and Northern
Resident communities (including SE Alaska and Bering Sea). Based on
sample sizes in studies to date, it is extremely unlikely that
transient or Northern Residents have a Southern Resident haplotype that
has gone undetected due to chance. Due to smaller sample sizes for
offshores, it is harder to rule out that offshores might contain the
Southern Resident haplotype in a small fraction of the population
(i.e., 10 percent), but it has yet to be detected. The Southern
Resident haplotype is shared with whales sampled off the Kamchatka
Peninsula in Russia and from Prince William Sound in Alaska (Barrett-
Lennard, 2000; Parsons et al., 2013); however, additional data can be
used to rule out the possibility that Lolita originated from these
other populations. Using microsatellite analysis, researchers assigned
Lolita to populations using different programs with varying
probabilities and assessed kinship (Hoelzel et al., 2007; Pilot et al.,
2010). In Pilot et al. (2010), Lolita was assigned to the Southern
Resident population with the highest probability (0.464) and with low
probability to Kamchatka (0.016) or SE Alaska residents (0.004). Tests
for kinship using microsatellite data found a presumed match between
Lolita and a member of the Southern Resident L pod based on one of four
tests, but it was not a close relationship (e.g., parent, offspring, or
full sibling). Lolita did not show potential kinship with individuals
of any other population. Using a different analysis, Pilot et al.
(2010) also assigned Lolita to a Southern Resident cluster and not to
the Kamchatka cluster. The microsatellite data do not appear to provide
conclusive evidence on their own to identify Lolita's population of
origin, but the data support the finding that she is a Southern
Resident.
The peer reviews concluded that the summary of our findings
regarding Lolita in our status review update (NMFS, 2013) likely
correctly concluded that Lolita is a Southern Resident and that, taken
together, the mtDNA and microsatellite DNA provide a strong case for
the assignment of Lolita to the Southern Resident population. While
some comments focused on individual test results to form conclusions,
we relied on all of the best available information in the petition,
public comments on the 90-day finding and the proposed rule, peer
review, peer reviewed journal articles, unpublished science reports,
and the recovery plan (NMFS, 2008), taken together, to inform our
internal review and conclusions. Based on the best available
information regarding the location of capture and genetic information,
we are confident that Lolita originated from the Southern Resident
population.
Comment 2: One commenter provided information from her study of the
specific acoustic call type produced by Lolita, matching Lolita's calls
to Southern Resident specific call types. The commenter suggested that
further identification of Lolita's calls could be matched with specific
matrilines. Other commenters noted that there is no statistically
significant or peer reviewed data or analysis that the calls recorded
opportunistically from Lolita match L pod calls. In addition,
commenters noted that the Ford (1987) paper cited in the status review
did not include specific information about Lolita and her calls. One
peer reviewer noted that additional information about the timing of the
recording of Lolita's calls and the origin of the whale sharing
Lolita's tank would shed light on whether Lolita was an L pod whale or
if she could have learned L pod calls from another whale.
[[Page 7384]]
Response: In the status review update (NMFS, 2013), the Ford (1987)
paper was cited to demonstrate that calls can be identified to
population and also to pod, and we acknowledge that it does not include
specific information about Lolita's calls. While the acoustic
information about Lolita's calls is not published in a peer reviewed
article, the personal communication by Candice Emmons does lend an
additional line of evidence that is consistent with Lolita originating
from the Southern Resident killer whale population. The study provided
by a commenter is also not a peer reviewed published article. In
addition, the peer review comments also raised uncertainty about
identifying Lolita by her acoustic calls based on the personal
communication. While we considered the anecdotal and unpublished
information on Lolita's acoustic calls, noting the uncertainty
surrounding them, we relied on the genetic data and capture location as
the primary support for Lolita's status as a member of the Southern
Resident killer whale population.
Comment 3: In addition to genetic and acoustic information,
Lolita's capture history was also mentioned by commenters and peer
reviewers as evidence that she came from the Southern Resident
population. One commenter noted photographs from the capture operation
were identified as Southern Residents and that members of different
communities have never been observed associating, concluding that all
of the whales captured at Penn Cove were members of the Southern
Resident community. One commenter, however, noted that the capture
history raised questions about Lolita's origin, mentioning that the
total number of whales in the area was too high to account for only the
Southern Residents and that L pod whales were photographed near the
operation but not in the net. The peer reviewers referenced the
sighting history of killer whales in the capture area as support for
Lolita's identification as a Southern Resident.
Response: We did not receive any photo-identification quality
photographs of the capture and have no specific documentation of the
captures beyond the information summarized in the Recovery Plan for
Southern Resident Killer Whales (NMFS, 2008) that attributes captures
from Penn Cove, Washington, to the Southern Resident population. One
peer reviewer noted the location of capture does not rule out that she
is a transient (but mtDNA makes this highly unlikely), and that the
capture location makes it highly unlikely that she is a Northern
Resident, offshore, Western Pacific, Alaska Resident or from a distant,
poorly known population. A review of the information raised in public
comments, the peer reviews, comments on the peer review plan, and other
available information finds this information continues to find the
capture information regarding Lolita consistent with her membership as
a Southern Resident. That review (Ford, 2014) notes that based on what
is known about the ranges of North Pacific killer whales, the Penn
Cove, WA capture location limits the possible populations of origin to
Southern Residents or transients which are commonly seen, or far less
likely to Northern Residents (only seen a handful of times in U.S.
waters of the Salish Sea) or offshores (only sighted six times in 30
years of observations and never south of Admiralty Inlet) (Krahn et
al., 2004; Ford, 2006; Dahlheim et al., 2008). Regular observations in
the Salish Sea have occurred since the mid-1970s, several years after
the capture in question, and it seems highly unlikely that the
distributions and habits of these populations would change dramatically
over that short period of time (Ford, 2014).
Comment 4: Several commenters noted that, morphologically, Lolita's
saddle patch patterns do not readily match the majority of saddle patch
patterns of the Southern Resident DPS, but they are more similar to
saddle patches of the Alaska and Bering Strait residents. One peer
reviewer suggested saddle patch and dorsal fin shape could be used to
further address Lolita's origin.
Response: Bain (1988) found differences between Northern and
Southern Resident saddle shapes and Baird and Stacey (1988) reported
different distributions of saddle shapes among residents and
transients. Baird and Stacey (1988) identified five different patterns,
with all five patterns present in resident killer whales. Lolita's
saddle shape appears to be consistent with the ``horizontal notch''
type. While this saddle patch type is seen in Alaska Residents, it is
more common in Southern Residents (Baird and Stacey, 1988). The
information above regarding sighting records and the capture location
includes an assessment by a peer reviewer, noting that it is highly
unlikely that Lolita is an Alaska Resident.
Comment 5: Several commenters reviewed the ESA section 4(a)(1)
factors and identified how they applied to Lolita. Other commenters
noted that none of the threats identified in the listing of the
Southern Resident killer whale DPS (i.e., food scarcity, vessels,
contaminants) apply to Lolita.
Response: In March 2011, we completed a 5-year review of the ESA
status of the Southern Resident killer whale DPS, concluding that no
change was needed in its listing status and that the Southern Resident
killer whale DPS would remain listed as endangered (NMFS, 2011). The
endangered status of the DPS is not the subject of the petitioned
action. The petition requests we include Lolita in the ESA listing of
Southern Residents and notes that an analysis of the five ESA section
4(a)(1) factors is not required to justify Lolita's inclusion in the
DPS and that Lolita's genetic heritage is sufficient to support her
inclusion in the listing. We agree that biological information
regarding Lolita's origin and consideration of the applicability of the
ESA to captive members of endangered species provide a sufficient basis
for our determination and, therefore, do not include a review of the
section 4(a)(1) factors for Lolita or the wild population in this
notice.
Captivity and Release
Comment 6: One commenter questioned why the ESA applied to Lolita
at all, considering she was held in captivity prior to December 28,
1973, and the date of the listing of the Southern Resident killer
whales.
Response: The commenter presumably refers to section 9(b) of the
ESA, 16 U.S.C. 1538(b)(1), which provides certain exemptions for
animals already held in captivity or a controlled environment on either
December 28, 1973, or the date of publication in the Federal Register
of the final regulation adding such species to the list of endangered
species, provided that such holding and any subsequent holding of the
animal is not in the course of a commercial activity.
In fact, this section is not a blanket exemption from the ESA for
any animal so held; rather, it only lifts the ban on two very specific
activities enumerated in subsections (a)(1)(A) and (G) of section 9:
import or export of such species, and violation of any regulation
pertaining to such species or to any threatened species. In other
words, all of the other prohibitions of section 9 apply to animals that
were held in captivity pre-ESA or pre-listing, including the
prohibitions on take as well as on interstate or foreign commerce. Any
import or export of Lolita that might be proposed in the future is
beyond the scope of this rulemaking. For additional discussion of ESA
section 9(b), see American Society for the Prevention of Cruelty to
Animals v. Ringling Brothers
[[Page 7385]]
and Barnum and Bailey Circus, 502 F.Supp. 2d 103 (2007).
Comment 7: Several commenters noted that the ESA does not allow for
the exclusion of captive members from a listed species based on their
captive status and referenced court cases (Safari Club International v.
Jewell and Alsea Valley Alliance v. Evans, cited below in response) and
recent USFWS notices regarding antelopes and chimpanzees that were
referenced in the proposed rule. In addition, commenters noted that if
Lolita is included in the listing, the ESA prohibitions on export,
take, and interstate commerce will apply to her.
Response: As the commenters note, several courts have held, and
NMFS agrees, that the ESA does not allow for captive held animals to be
assigned separate legal status from their wild counterparts on the
basis of their captive status or through designation as a separate DPS
(Safari Club International v. Jewell, 960 F.Supp. 2d 17 (D.D.C. 2013);
Alsea Valley Alliance v. Evans, 161 F. Supp. 2d 1154 (D.Or. 2001). As
noted in this final rule, as well as in recent regulations addressing
captive antelopes (78 FR 33790; June 5, 2013) and a proposed rule for
chimpanzees (78 FR 35201; June 12, 2013), captive members of a species
have the same legal status as the species as a whole. Finally, as the
commenters note, captive members of a listed species are also subject
to the relevant provisions of section 9 of the ESA as warranted.
Comment 8: One commenter expressed concern that including Lolita in
the ESA listing would result in a violation of the Fifth Amendment,
denying the property owners their rights without satisfying the
Constitution's public use and just compensation requirements. One
commenter supported their opposition to including Lolita in the ESA
listing by citing examples of how extending regulations to privately
owned members of a listed species could undermine private efforts to
avoid extinction and recover species through private governance.
Commenters also noted that financial considerations should not be
considered in listing decisions.
Response: First, section 4(b)(1)(A) of the ESA and its legislative
history provides that listing decisions be based ``solely'' on the best
scientific and commercial data available without reference to economic
costs or private party impacts (H.R. Rep. No. 97-567, at 12, 1982
U.S.C.C.A.N. 2807, 2812). Second, to the extent there are concerns
about specific activities (including acts supporting conservation)
associated with listed species, these issues are better evaluated in
the context of a specific permit request and through the section 10
permit process, which provides an avenue for defining, evaluating, and
authorizing specific activities (50 CFR 222.301 et seq.). Accordingly,
speculating about whether there are activities that property owners may
wish to take is beyond the scope of this rule.
Comment 9: One commenter took issue with our assertion that if
Lolita was included in the ESA listing, we would not seek to amend
critical habitat to include consideration of her or her captive
environment. The commenter cited the requirement to designate critical
habitat with the listing of a species in section 4(a)(3)(A) of the ESA.
Response: NMFS designated critical habitat for the Southern
Resident killer whale DPS on November 29, 2006 (71 FR 69054). NMFS
interprets critical habitat to comprise the habitat used by the species
in the wild, not the artificial surroundings of a particular species
member in captivity, because those areas do not include relevant
primary constituent elements of critical habitat (70 FR 52630;
September 2, 2005). Accordingly, we do not intend to amend the existing
critical habitat designation for Southern Resident killer whales with
respect to Lolita.
Comment 10: We received many comments addressing the type and scope
of activities that might trigger section 9 concerns and/or warrant
consideration for a section 10 permit. These comments took varying
positions on the scope of activities that might fall within the
category of allowable captive care activities.
Response: In the proposed rule, we said that, depending on the
circumstances, we would likely not find continued possession, care, and
maintenance of a captive animal to be a violation of ESA section 9 (and
therefore, such activities would not require a section 10 permit). Our
discussion in the proposed rule was intended to be a general indication
of our views, not factual findings on Lolita's actual circumstances or
any proposals for future activities. Such findings are beyond the scope
of this listing rule.
We appreciate the concerns raised by the many comments regarding
how the ESA section 9 prohibitions might apply to Lolita's particular
circumstances. We believe these comments demonstrate the need for a
more focused evaluation of these factors, which is more appropriately
performed as part of a permit application process as opposed to this
listing rule. Should the Miami Seaquarium apply for an ESA section 10
permit, the process would involve a Federal Register notice of receipt
followed by a public comment period.
Comment 11: Commenters raised questions about the Miami Seaquarium
conducting commercial activity with Lolita, stating their belief that
section 9(b) of the ESA allows for captives to remain in captivity so
long as they are not held or used for purposes of commercial activity.
Other commenters stated that there is nothing illegal about exhibiting
endangered animals for a fee.
Response: Some commenters may have misinterpreted section 9(b) in
this regard. As noted above, section 9(b) is a very limited exclusion
from the prohibition on import and export, as well as certain
regulatory requirements not applicable here. Any future proposal to
import or export Lolita is beyond the scope of this rule, and so we
need not further address the 9(b) exemption, including its clause
regarding commercial activity, at this time.
Comment 12: One commenter urged us to acknowledge that interstate
movement of Lolita or any other captive listed species merely for
display or as part of an animal exhibition would not require a permit
under the ESA, citing U.S.C. 1538(a)(E) and 50 CFR 17.3.
Response: At this time, the Miami Seaquarium has not presented any
proposal to move Lolita, regardless of purpose, so we will not address
this further in this listing rule, other than to note that the cited
CFR provision is a regulation promulgated by the USFWS, and is
therefore applicable to species under their jurisdiction.
Comment 13: Commenters expressed concern over captivity of killer
whales in general and about Lolita's current care at the Miami
Seaquarium under the purview of APHIS under AWA. Other commenters noted
the high level of care provided to Lolita at the Miami Seaquarium.
Response: As noted above, Lolita's current captive care
requirements are regulated by APHIS under the AWA and are currently the
subject of ongoing litigation (Animal Legal Defense Fund et al. v.
Elizabeth Goldentyer, USDA and Marine Exhibition Corporation No. 14-
12260 (11th Circuit Court of Appeals 2014)). Specific AWA captive care
requirements are not under NMFS jurisdiction and are beyond the scope
of our response to the petition. Therefore, comments regarding AWA
compliance are not addressed in this final rule.
Comment 14: Many comments supported Lolita's transfer to a sea pen
or release from captivity into her home waters. Some commenters, while
in favor of Lolita's ultimate release, argued that any decision on this
issue in the
[[Page 7386]]
absence of a specific proposal is premature. Comments on whether there
would be any conservation benefit to the conservation of wild killer
whales from Lolita's release were mixed. Some comments identified
benefits to Lolita and to the wild Southern Resident killer whale
population, such as her ability to aid in the care of young whales
(i.e., alloparenting). Others were against any relocation efforts,
claiming that there would be no conservation benefits to wild whales
and noting Lolita currently has a high level of care, contributes to
educating the public, and there are risks to Lolita and the wild
population associated with transport and release. One commenter noted
that regulations regarding marine mammal rehabilitation under the MMPA
declare that a marine mammal that has been in human care for 2 or more
years is presumptively non-releaseable.
Response: As noted above, the Miami Seaquarium has not presented
any proposal to move (or release) Lolita. As for any future proposal to
release her, we indicated in the proposed rule that there were certain
activities that we believe could result in violations of section 9 of
the ESA, specifically including ``releasing a captive animal into the
wild.'' 79 FR at 4318 (January 27, 2014). We based this on our proposed
rule listing five species of sturgeon (since finalized at 79 FR 31222,
June 2, 2014). After taking into account the numerous comments on this
topic, and examining our existing regulations, policies and practices,
we have decided to elaborate on our views in this final rule. Releasing
captive marine mammals to the wild is not without risk. Issues of
concern include: disease transmission and/or unwanted genetic exchange
between released animals and wild stocks; the ability of released
animals to adequately forage and defend themselves from predators; and
any behavioral patterns developed in captivity that could affect the
social behavior of wild animals, as well as the social integration of
the released animals.
In fact, as one commenter noted, NMFS' MMPA regulations address a
presumption of non-releasability, as well as dictate legal requirements
under the MMPA for any proposal to release a captive animal. First, 50
CFR 216.27(a)(1)(iii), addressing stranded marine mammals, states that
the animal's potential for survival in the wild must be evaluated at 6-
month intervals, ``until 24 months from capture or import, at which
time there will be a rebuttable presumption that release to the wild is
not feasible.'' Second, 50 CFR 216.35(e) states: ``Captive marine
mammals shall not be released into the wild unless specifically
authorized by the Office Director under a scientific research or
enhancement permit.''
The issues surrounding any release of Lolita to the wild are
numerous and complex and are not ripe for analysis in this listing
rule. Such issues would be more appropriately evaluated in the context
of a specific section 10 permit application. Any such process would
include rigorous review by the scientific community, the Marine Mammal
Commission, and the public, and be subject to an associated NEPA
analysis, prior to action being taken.
Changes From the Proposed Rule
There are no changes from the proposed amendment to the ESA listing
of the Southern Resident killer whale DPS in this final rule. This
final rule implements the amendment to the listing language, removing
the exclusion for captive whales from the regulatory description of the
Southern Resident killer whale DPS. The public comments provided
opposing positions on this approach, as well as Lolita's status as a
member of the Southern Resident killer whale population. The peer
reviews supported Lolita's status as a member of the Southern Resident
killer whale population. See the Summary of Peer Review and Public
Comments Received section above and the Final Determination and
Amendment to Listing section below for information on the additional
data that support the conclusion that captive members should be
included in the listing and the determination that best available
science supports Lolita's status as a member of the Southern Resident
killer whale population and therefore the ESA-listed DPS.
Determination of Taxon and DPS
Based on the best information available, we previously concluded,
with advice from the 2004 BRT (Krahn et al., 2004), that the Southern
Resident killer whale population (J, K, and L pods) met the two
criteria of the DPS policy (discreteness and significance) and
constituted a DPS of the North Pacific Resident subspecies. A detailed
analysis of (1) the reference taxon for consideration under the DPS
policy, (2) the discreteness of the Southern Resident population from
other populations within that taxon, and (3) the significance of the
Southern Resident population to that taxon was included in our 12-month
determination that the petition to delist was not warranted (78 FR
47277; August 5, 2013) and is summarized below. Based on our recent
status review and in response to a petition to delist the Southern
Resident killer whale DPS, we concluded that the best available
scientific information indicates that, similar to our 2005 rulemaking
when we listed the Southern Resident DPS, the North Pacific Resident
subspecies is the appropriate reference taxon for considering whether
the Southern Resident killer whale population is discrete and
significant. In our 2005 rulemaking we concluded there was strong
evidence that the Southern Resident killer whale population is discrete
from other North Pacific Resident killer whale populations as defined
by the 1996 DPS policy. The new information subsequent to 2004, such as
recent genetic studies, is consistent with and generally strengthens
the conclusion that the Southern Resident killer whale population is a
discrete population within the North Pacific Resident taxon. As in
2004, all the available information clearly indicates that the Southern
Resident population is discrete from other populations in the North
Pacific resident subspecies. In addition, we concluded that the new
information on genetics and behavioral and cultural diversity available
since 2004 was consistent with or strengthens the 2004 BRT's conclusion
that the Southern Resident killer whale population meets the
significance criterion of the DPS policy. In summary, in our 12-month
finding that delisting was not warranted, we concluded that members of
the Southern Resident killer whale population are discrete from other
populations within the North Pacific Resident killer whale taxon and
significant with respect to the North Pacific Resident killer whale
taxon and therefore comprise a valid DPS which remains listed as
endangered (78 FR 47277; August 5, 2013).
Final Determination and Amendment to Listing
The petition maintains that Lolita is a member of the Southern
Resident killer whale population and states that she must, therefore,
be included in the listed DPS. As summarized above, our consideration
of the petitioned action focuses on biological information regarding
Lolita's genetic heritage and the application of the ESA to captive
members of a listed species or DPS. The petitioners contend that Lolita
was taken from L pod during captures on August 8, 1970, in Penn Cove,
approximately 50 miles (80 km) north of Seattle, Washington. The peer
reviewers referenced the capture location and sighting history of
different populations, in addition to other information (i.e.,
[[Page 7387]]
genetics), to support their conclusions that Lolita most likely came
from the Southern Resident population. The petition notes that Lolita's
mother is believed to be L25, an adult female Southern Resident killer
whale who remains in the wild, and that Lolita makes the unique calls
of the L25 subpod. In our recent status review update (NMFS, 2013), we
cited genetic analysis completed since the original 2005 listing, that
indicates Lolita has a genotype consistent with a Southern Resident
origin (Hoelzel et al., 2007; Hoelzel, personal communication), and we
noted that Lolita's acoustic calls are typical of L pod (Ford, 1987;
Candice Emmons, personal communication). The status review update
(NWFSC, 2013) also cites information in Pilot et al. (2010). As
described above, in support of the DPS determination for Southern
Resident killer whales, recent genetic studies all indicate that the
Southern Resident population is significantly differentiated and there
is a high degree of reproductive isolation from other resident
populations that comprise the North Pacific Resident subspecies.
As described above in the response to comments, the peer reviewers
identified that mtDNA tests are very likely diagnostic of natal
populations. The mtDNA control region sequence is fixed for a single
haplotype within most killer whale populations in the North Pacific.
Lolita has the haplotype for Southern Residents, which is distinct from
the haplotypes found in transient, offshore, and Northern Resident
communities (including SE Alaska and Bering Sea). Based on sample sizes
in studies to date, it is extremely unlikely that transient or Northern
Residents have a Southern Resident haplotype that has gone undetected
due to chance. Due to smaller sample sizes for offshores, it is harder
to rule out that offshores might contain the Southern Resident
haplotype in a small fraction of the population (i.e., 10 percent), but
it has yet to be detected. The Southern Resident haplotype is shared
with whales sampled off the Kamchatka Peninsula in Russia and from
Prince William Sound in Alaska (Barrett-Lennard, 2000; Parsons et al.,
2013), but additional data can be used to rule out the possibility that
Lolita originated from these other populations. Using microsatellite
analysis, researchers assigned Lolita to population using different
programs with varying probabilities and assessed kinship (Hoelzel et
al., 2007; Pilot et al., 2010). In Pilot et al. (2010), Lolita was
assigned to the Southern Resident population with the highest
probability (0.464) and with low probability to Kamchatka (0.016) or SE
Alaska residents (0.004). Tests for kinship found a putative match
between Lolita and a member of the Southern Resident L pod based on one
of four tests, but it was not a close relationship (e.g., parent,
offspring, or full sibling). Lolita did not show potential kinship with
individuals of any other population. Using a different analysis, Pilot
et al. (2010) also assigned Lolita to a Southern Resident cluster and
not to the Kamchatka cluster. The microsatellite data do not appear to
provide conclusive evidence on their own to identify Lolita's
population of origin, but they are consistent with her being a Southern
Resident.
The peer review conclusions were that our status review update
(NMFS, 2013) was overly simplistic, but likely correctly concluded that
Lolita is a Southern Resident and that, taken together, the mtDNA and
microsatellite DNA data provide a strong case for the assignment of
Lolita to the Southern Resident population. As described above, we
relied on information in the petition, public comments on the 90-day
finding and the proposed rule, peer review and best available
information, including peer reviewed journal articles and unpublished
science reports and the recovery plan (NMFS, 2008) to inform our
internal review and conclusions. Similar to the peer reviews and as
raised in public comments, we acknowledge the uncertainty inherent in
individual test results and observations; however, based on all of the
best available scientific information, taken together, including
results from multiple genetic studies, as well as other lines of
evidence regarding capture and sighting history, we can be confident
that Lolita originated from the Southern Resident population (Ford,
2014). Differences in acoustic behavior between populations of resident
killer whales also support the conclusion that Southern Resident killer
whales are discrete and significant and, therefore, qualify as a DPS.
Ford (1987) describes killer whale acoustic calls and how they can be
identified to population and even to pod. While there is anecdotal
information that Lolita shares acoustic characteristics with the
members of the Southern Resident killer whale DPS found in the wild,
this evidence is not as strong as the genetic data. In addition,
morphological data, such as saddle patch pattern, are also consistent
with, but not conclusive of, Lolita being a Southern Resident. This
best available science supports Lolita's status as a member of the
Southern Resident killer whale population.
Some commenters contend that Lolita not be included in the Southern
Resident killer whale DPS, similar to other wild whales that are
members of the North Pacific Resident subspecies (i.e., Northern
Resident and Alaska Resident killer whale populations). These
commenters fail to recognize the previously discussed best available
science defining the genetic characteristics that Lolita shares with
the Southern Resident killer whale DPS and often highlighted individual
test results rather than all of the available scientific information
taken together. We find the multiple genetic characteristics constitute
compelling lines of evidence that render Lolita and other members of
the Southern Resident killer whale DPS discrete from and significant to
the North Pacific Resident subspecies (NMFS, 2013; Ford, 2014).
Additionally, while the ESA authorizes the listing, delisting, or
reclassification of a species, subspecies, or DPS of a vertebrate
species, it does not authorize the exclusion of the members of a subset
or portion of a listed species, subspecies, or DPS from a listing
decision. In 2001, the U.S. District Court in Eugene, Oregon (Alsea
Valley Alliance v. Evans, 161 F. Supp.2d 1154 (D. Or. 2001)) (Alsea),
ruled that once we had identified and listed a DPS (for Oregon Coast
coho), the ESA did not allow listing only a subset (that which excluded
10 captive hatchery stocks) of that DPS. Accordingly, this case does
not authorize the exclusion of Lolita from the Southern Resident Killer
Whale DPS listing based on the best available science supporting her
membership in the DPS.
Other comments note that there are other characteristics, such as
behavior and habitat use, that Lolita does not share with the other
wild members of the Southern Resident killer whales and suggest that
NMFS could exercise its discretion to identify a separate captive only
DPS. However, legislative history surrounding the 1978 amendments to
the ESA that gave the Services the authority to identify DPSs indicates
that Congress intended identification of DPSs to be used for the
identification of wild populations, not separation of captive held
specimens from wild members of the same taxonomic species (see
Endangered Species Act Oversight: Hearing Before Senate Subcommittee on
Resource Protection, Senate Committee on Environment and Public Works,
95th Cong. 50 (July 7, 1977)). Additionally, these arguments fail to
adhere to Congress' directive to the Services that the authority to
designate DPSs be exercised ``sparingly'' (Senate Report
[[Page 7388]]
151, 96th Congress, 1st Session). Finally, NMFS' decision making
relevant to identifying a captive only DPS, in this context, is
discretionary and not subject to judicial review (Safari Club
International v. Jewell, 960 F. Supp. 2d 17 (DDC 2013)).
As described in the proposed rule (79 FR 4313; January 27, 2014),
the ESA does not support the exclusion of captive members from a
listing based solely on their captive status. On its face the ESA does
not treat captives differently. Rather, specific language in section 9
and section 10 of the ESA presumes their inclusion in the listed
entity, and captives are subject to certain exemptions to section 9.
Section 9(a)(1)(A)-(G) of the ESA applies to endangered species
regardless of their captive status. However, section 9(b) provides
certain exemptions from the 9(a)(1)(A) and (a)(1)(G) prohibitions for
listed animals held in captivity or in a controlled environment as of
the date of the species' listing (or enactment of the ESA), provided
the holding in captivity and any subsequent use is not in the course of
commercial activity. Additionally, section 9(b)(2) refers to captive
raptors and identifies that the prohibitions in 9(a)(1) shall not apply
to raptors legally held in captivity. Section10(a)(1)(A) of the ESA
allows issuance of permits to ``enhance the propagation or survival''
of the species. This demonstrates that Congress recognized the value of
captive holding and propagation of listed species held in captivity but
intended that such specimens would be protected under the ESA, with
these activities generally regulated by permit.
We have specifically identified captive members as part of the
listed unit during listing actions, such as for endangered smalltooth
sawfish (68 FR 15674; April 1, 2003), and endangered Atlantic sturgeon
(77 FR 5914; February 6, 2012), and in the final listing of five
species of foreign sturgeon (79 FR 31222; June 2, 2014). Further, based
upon the purposes of the ESA and its legislative history, courts have
held and the USFWS has recently concluded that the ESA does not allow
captive animals to be assigned different legal status from their wild
counterparts on the basis of their captive status (Safari Club
International v. Jewell, 960 F. Supp. 2d 17 (DDC 2013)). Subsequent to
the submission of the petition regarding Lolita, USFWS published a
proposed rule to amend the listing status of captive chimpanzees, so
that all chimpanzees (wild and captive) would be listed as endangered
(78 FR 35201; June 12, 2013). USFWS also published a 12-month finding
that delisting the captive members of three listed antelope species was
not warranted (78 FR 33790; June 5, 2013).
In a recent notice announcing a Final Policy of Interpretation of
the Phrase ``Significant Portion of Its Range (SPR)'' in the Endangered
Species Act's Definitions of ``Endangered Species'' and ``Threatened
Species'' (79 FR 37578; July 1, 2014), the Services also confirmed the
legal status of captive members of listed species. The notice explains,
with regard to species found in captivity, the Services consider a
captive population to have no ``range'' separate from that of the
species to which it belongs (captive populations cannot be considered a
SPR). The notice also states ``captive members have the same legal
status as the species as a whole.''
Based on the preceding discussion, the information submitted during
the public comment period, the peer reviews, and best available science
and information, we find that captive members of the Southern Resident
killer whale population should not be excluded from the listed Southern
Resident killer whale DPS based on their captive status. Accordingly,
this rule removes the exclusion for captive whales in the regulatory
language describing the Southern Resident killer whale DPS. Our finding
is consistent with the recent USFWS conclusions regarding the status of
captive animals under the ESA and also with the Marine Mammal
Commission recommendation to adopt a policy consistent with the USFWS
in the proposed chimpanzee listing rule and treat all biological
members of the Southern Resident killer whales as part of the DPS,
regardless of whether those individuals are in the wild or in captivity
(Marine Mammal Commission letter, August 13, 2013).
As part of the 2005 ESA listing of the Southern Resident killer
whale DPS (70 FR 69903; November 18, 2005), we conducted an analysis of
the five ESA section 4(a)(1) factors and concluded that the DPS was in
danger of extinction and listed it as endangered. In March 2011, we
completed a 5-year review of the ESA status of the Southern Resident
killer whale DPS, concluding that no change was needed in its listing
status and that the Southern Resident killer whale DPS would remain
listed as endangered (NMFS, 2011). The petition and several public
comments included an analysis of the five ESA section 4(a)(1) factors
with respect to Lolita, although petitioners note that the analysis is
not required to justify Lolita's inclusion in the DPS and that Lolita's
genetic heritage is sufficient to support her inclusion in the listing.
We agree that biological information regarding Lolita's origin and
consideration of the applicability of the ESA to captive members of
endangered species provide a sufficient basis for our determination
and, therefore, do not include a review of the section 4(a)(1) factors
for Lolita or the wild population.
While progress toward recovery has been achieved since the listing,
as described in the 5-year review, the status of the DPS remains as
endangered. Since the 5-year review was completed, additional actions
have been taken to address threats, such as regulations to protect
killer whales from vessel impacts (76 FR 20870; April 14, 2011),
completion of a scientific review of the effects of salmon fisheries on
Southern Resident killer whales (Hilborn, 2012), and ongoing technical
working groups with the Environmental Protection Agency to assess
contaminant exposure. However, the population growth outlined in the
biological recovery criteria and some of the threats criteria have not
been met. We have no new information that would change the
recommendation in our 5-year review that the Southern Resident killer
whale DPS remain classified as endangered (NMFS, 2011). This final rule
amends the language describing the Southern Resident killer whale DPS
by removing the exclusion of captive whales. With this change, Lolita,
a female killer whale captured from the Southern Resident killer whale
population in 1970, is not excluded from the Southern Resident killer
whale DPS due to her captive status.
Effects of Amendment to Listing
Conservation measures provided for species listed as endangered or
threatened under the ESA include concurrent designation of critical
habitat if prudent and determinable (16 U.S.C. 1533(a)(3)(A)); recovery
plans and actions (16 U.S.C. 1536(f)); Federal agency requirements to
consult with NMFS and to ensure its actions do not jeopardize the
species or result in adverse modification or destruction of critical
habitat should it be designated (16 U.S.C. 1536); and prohibitions on
taking (16 U.S.C. 1538). Following the listing, we designated critical
habitat and completed a recovery plan for the Southern Resident killer
whale DPS. We issued a final rule designating critical habitat for the
Southern Resident killer whale DPS November 29, 2006 (71 FR 69055). The
designation includes three specific areas: (1) The Summer Core Area in
Haro Strait and waters around the San Juan Islands; (2) Puget Sound;
and (3) the Strait of Juan de Fuca, which together comprise
approximately 2,560
[[Page 7389]]
square miles (6,630 square km). The designation excludes areas with
water less than 20 feet (6.1 m) deep relative to extreme high water.
The designated critical habitat will not be affected by removing the
exclusion of captive whales from the regulatory language describing the
Southern Resident killer whale DPS. As the USFWS identified in its
recent proposed chimpanzee rule, there is an ``anomaly of identifying
the physical and biological features that would be essential to the
conservation of a species consisting entirely of captive animals in an
artificial environment'' (78 FR 35201; June 12, 2013). This observation
also holds for a listed entity with only one captive member. In
addition, the recent notice announcing a final policy interpreting
Significant Portion of its Range under the ESA notes the Services
consider a captive population to have no ``range'' separate from that
of the species to which it belongs (79 FR 37578; July 1, 2014). We do
not intend to modify the critical habitat designation to include
consideration of Lolita and her captive environment.
After engaging stakeholders and providing multiple drafts for
public comment, we announced the Final Recovery Plan for the Southern
Resident killer whale DPS on January 24, 2008 (73 FR 4176). Lolita's
capture and captivity is mentioned in the recovery plan; however, the
recovery actions in the plan are focused on addressing the threats to
and the recovery of the wild population. As the recovery plan is
updated in the future, we will consider including an update that Lolita
is included in the DPS.
Sections 7(a)(2) of the ESA requires Federal agencies to ensure
that activities they authorize, fund, or carry out are not likely to
jeopardize the continued existence of a listed species, or to adversely
modify critical habitat. In the USFWS proposed rule for chimpanzees (78
FR 35201; June 12, 2013), USFWS identifies that ``the section 7
consultation process is not well suited to analysis of adverse impacts
posed to a purely captive-held group of specimens given that such
specimens are maintained under controlled, artificial conditions.''
This observation also holds for a listed entity with only one captive
member. Previous guidance on examples of Federal actions that have the
potential to impact Southern Resident killer whales was focused on
activities that may affect wild whales. Additional considerations of
actions that have the potential to affect Southern Resident killer
whales, including Lolita, will be considered along with prohibitions on
activities that affect the Southern Resident killer whale DPS. Some of
these considerations are discussed below.
Take Prohibitions and Identification of Those Activities That Might
Constitute a Violation of Section 9 of the ESA
On July 1, 1994, NMFS and USFWS published a policy (59 FR 34272)
that requires us to identify, to the maximum extent practicable at the
time a species is listed, those activities that would or would not
constitute a violation of section 9 of the ESA. The ESA does not
prohibit possession of animals lawfully taken into captivity, so a
permit is required only if the person possessing the animal intends to
engage in an otherwise prohibited act. Prohibited activities for ESA-
listed endangered species include, but are not limited to: (1) ``take''
of such species, as defined in the ESA (including to harass, harm,
pursue, hunt, shoot, wound, kill, trap, capture, or collect, or attempt
to engage in any such conduct); (2) delivering, receiving, carrying,
transporting, or shipping in interstate or foreign commerce, in the
course of a commercial activity, any such species; or (3) selling or
offering for sale in interstate or foreign commerce any such species.
In the proposed rule, we said that, depending on the circumstances,
we would not likely find continued possession, care, and maintenance of
a captive animal to be a violation of section 9 (and that therefore,
such activities would not require a section 10 permit). As noted above,
we received numerous comments addressing the types of activities that
might trigger section 9 concerns and/or warrant consideration for a
section 10 permit. We believe these comments demonstrate the need for a
more focused evaluation of these factors, which is more appropriately
performed as part of a permit application process as opposed to this
listing rule.
Likewise, we indicated in the proposed rule certain activities that
we believe could result in violations of section 9 of the ESA,
specifically including ``releasing a captive animal into the wild.'' 79
FR at 4318 (January 27, 2014). We based this on our proposed rule
listing five species of sturgeon (since finalized at 79 FR 31222, June
2, 2014).
In this final rule, NMFS notes that issues surrounding any release
of Lolita to the wild are numerous and complex and are not ripe for
analysis in this listing rule. Such issues would be better evaluated in
the context of a specific section 10 permit application. Any such
process would include rigorous review by the scientific community, the
Marine Mammal Commission, and the public, and be subject to an
associated NEPA analysis, prior to action being taken.
References Cited
The complete citations for the references used in this document can
be obtained by contacting NMFS (See ADDRESSES and FOR FURTHER
INFORMATION CONTACT) or on our Web page at: https://www.westcoast.fisheries.noaa.gov/protected_species/marine_mammals/killer_whale/lolita_petition.html.
Information Quality Act and Peer Review
In December 2004, the Office of Management and Budget (OMB) issued
a Final Information Quality Bulletin for Peer Review establishing
minimum peer review standards, a transparent process for public
disclosure of peer review planning, and opportunities for public
participation. The OMB Bulletin, implemented under the Information
Quality Act (Public Law 106-554), is intended to enhance the quality
and credibility of the Federal government's scientific information, and
applies to influential or highly influential scientific information
disseminated on or after June 16, 2005. To satisfy our requirements
under the OMB Bulletin, we obtained independent peer review of the
information on Lolita in our status review update (NMFS, 2013). Four
independent specialists were selected from the academic and scientific
community, Federal and state agencies, and the private sector for this
review (with two respondents). All peer reviewer comments were
addressed in this final rule. The peer review process is detailed at:
https://www.cio.noaa.gov/services_programs/prplans/ID261.html.
Classification
National Environmental Policy Act (NEPA)
The 1982 amendments to the ESA, in section 4(b)(1)(A), restrict the
information that may be considered when assessing species for listing.
Based on this limitation of criteria for a listing decision and the
opinion in Pacific Legal Foundation v. Andrus, 657 F. 2d 829 (6th Cir.
1981), we have concluded that NEPA does not apply to ESA listing
actions. (See NOAA Administrative Order 216-6.)
Executive Order 12866, Regulatory Flexibility Act, and Paperwork
Reduction Act
As noted in the Conference Report on the 1982 amendments to the
ESA, economic impacts cannot be considered
[[Page 7390]]
when assessing the status of a species. Therefore, the economic
analysis requirements of the Regulatory Flexibility Act are not
applicable to the listing process. In addition, this final rule is
exempt from review under Executive Order 12866. This final rule does
not contain a collection-of-information requirement for the purposes of
the Paperwork Reduction Act.
Executive Order 13122, Federalism
In accordance with E.O. 13132, we determined that this final rule
does not have significant federalism effects and that a federalism
assessment is not required. In keeping with the intent of the
Administration and Congress to provide continuing and meaningful
dialogue on issues of mutual state and Federal interest, this final
rule will be shared with the relevant state agencies in each state in
which the species is believed to occur.
List of Subjects in 50 CFR Part 224
Administrative practice and procedure, Endangered and threatened
species, Reporting and recordkeeping requirements.
Dated: February 4, 2015.
Eileen Sobeck,
Assistant Administrator for Fisheries, National Marine Fisheries
Service.
For the reasons set out in the preamble, 50 CFR part 224 is amended
as follows:
PART 224--ENDANGERED MARINE AND ANADROMOUS SPECIES
0
1. The authority citation for part 224 continues to read as follows:
Authority: 16 U.S.C. 1531-1543 and 16 U.S.C. 1361 et seq.
0
2. In Sec. 224.101, in the table in paragraph (h), revise the entry
for ``Whale, killer (Southern Resident DPS)'' to read as follows:
Sec. 224.101 Enumeration of endangered marine and anadromous species.
* * * * *
(h) * * *
----------------------------------------------------------------------------------------------------------------
Species\1\
------------------------------------------------------------------ Citation(s) for Critical
Description of listing habitat ESA Rules
Common name Scientific name listed entity determination(s)
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Marine Mammals
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Whale, killer (Southern Orcinus orca.... Killer whales [Insert citation] 226.206 224.103
Resident DPS). from the J, K, 2/10/2015.
and L pods.
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\1\ Species includes taxonomic species, subspecies, distinct population segments (DPSs) (for a policy statement,
see 61 FR 4722, February 7, 1996), and evolutionarily significant units (ESUs) (for a policy statement, see 56
FR 58612, November 20, 1991).
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[FR Doc. 2015-02604 Filed 2-9-15; 8:45 am]
BILLING CODE 3510-22-P