Endangered and Threatened Wildlife and Plants; Final Rule To List the Chambered Nautilus as Threatened Under the Endangered Species Act, 48976-48985 [2018-21114]
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48976
Federal Register / Vol. 83, No. 189 / Friday, September 28, 2018 / Rules and Regulations
paragraph (c)(4) of this section, a State
may waive the requirements in
§ 383.93(a)(1) and (c)(4) that an
applicant must pass a specialized
knowledge test, described in § 383.121,
for a hazardous materials (H)
endorsement. States must continue to
meet the requirements for a hazardous
materials endorsement in subpart I of
this part.
(4) Conditions and limitations. A
current or former military service
member applying for waiver of the
driving skills test or the specialized
knowledge test for a passenger carrier
endorsement, the knowledge test for the
tank vehicle endorsement, or the
knowledge test for the hazardous
materials endorsement, must certify and
provide evidence that, during the 1-year
period immediately prior to the
application, he/she:
(i) Is or was regularly employed in a
military position requiring operation of
a passenger CMV, if the applicant is
requesting a waiver of the knowledge
and driving skills test for a passenger
endorsement; operation of a tank
vehicle, if the applicant is requesting a
waiver of the knowledge test for a tank
vehicle endorsement; or transportation
of hazardous materials, if the applicant
is requesting a waiver of the knowledge
test for a hazardous materials
endorsement;
(ii) Has not simultaneously held more
than one civilian license (in addition to
a military license);
(iii) Has not had any license
suspended, revoked, or cancelled;
(iv) Has not had any convictions for
any type of motor vehicle for the
disqualifying offenses contained in
§ 383.51(b);
(v) Has not had more than one
conviction for any type of motor vehicle
for serious traffic violations contained
in § 383.51(c); and
(vi) Has not had any conviction for a
violation of military, State or local law
relating to motor vehicle traffic control
(other than a parking violation) arising
in connection with any traffic crash, and
has no record of a crash in which he/
she was at fault.
■ 4. Revise § 383.79 to read as follows:
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§ 383.79 Driving skills testing of out-ofState students; knowledge and driving
skills testing of military personnel.
(a) CDL applicants trained out-ofState—(1) State that administers the
driving skills test. A State may
administer its driving skills test, in
accordance with subparts F, G, and H of
this part, to a person who has taken
training in that State and is to be
licensed in another United States
jurisdiction (i.e., his or her State of
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domicile). Such test results must be
transmitted electronically directly from
the testing State to the licensing State in
a direct, efficient and secure manner.
(2) The State of domicile. The State of
domicile of a CDL applicant must accept
the results of a driving skills test
administered to the applicant by any
other State, in accordance with subparts
F, G, and H of this part, in fulfillment
of the applicant’s testing requirements
under § 383.71, and the State’s test
administration requirements under
§ 383.73.
(b) Active duty military service
members. An active-duty military
service member may apply for a CLP or
a CDL in the State where the individual
is stationed but not domiciled if the
requirements of this section are met.
(1) Role of State of duty station. (i)
Upon prior agreement with the State of
domicile, a State where active-duty
military service members are stationed,
but not domiciled, may accept an
application for a CLP or CDL, including
an application for waiver of the
knowledge test or driving skills test
prescribed in §§ 383.23(a)(1) and
383.25(a)(3), from such a military
service member who:
(A) Is regularly employed or was
regularly employed within the last year
in a military position requiring
operation of a CMV;
(B) Has a valid driver’s license from
his or her State of domicile;
(C) Has a valid active-duty military
identification card; and
(D) Has a current copy of either the
service member’s military leave and
earnings statement, or his or her orders.
(ii) A State where active-duty military
service members are stationed, but not
domiciled, may:
(A) Administer the knowledge and
driving skills tests to the military
service member, as appropriate, in
accordance with subparts F, G, and H of
this part, if the State of domicile
requires those tests; or
(B) Waive the knowledge and driving
skills tests in accordance with § 383.77,
if the State of domicile has exercised the
option to waive those tests; and
(C) Destroy the military service
member’s civilian driver’s license on
behalf of the State of domicile, unless
the latter requires the driver’s license to
be surrendered to its own driver
licensing agency.
(iii) The State of duty station must
transmit to the State of domicile by a
direct, secure, and efficient electronic
system the completed application, any
supporting documents, and—if the State
of domicile has not exercised its waiver
option—the results of any knowledge
and driving skills administered.
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(2) Role of State of domicile. Upon
completion of the applicant’s
application pursuant to § 383.71 and
any testing administered by the State of
duty station pursuant to §§ 383.71 and
383.73, the State of domicile of the
military service member applying for a
CLP or CDL may:
(i) Accept the completed application,
any supporting documents, and the
results of the knowledge and driving
skills tests administered by the State of
duty station (unless waived at the
discretion of the State of domicile); and
(ii) Issue the applicant a CLP or CDL.
PART 384—STATE COMPLIANCE
WITH COMMERCIAL DRIVER’S
LICENSE PROGRAM
5. The authority citation for part 384
is revised to read as follows:
■
Authority: 49 U.S.C. 31136, 31301 et seq.,
and 31502; secs. 103 and 215 of Pub. L. 106–
59, 113 Stat. 1753, 1767; sec. 32934 of Pub.
L. 112–141, 126 Stat. 405, 830; sec. 5401 and
7208 of Pub. L. 114–94, 129 Stat. 1312, 1546,
1593; and 49 CFR 1.87.
6. Amend § 384.301 by adding
paragraph (l) to read as follows:
■
§ 384.301 Substantial compliance—
general requirements.
*
*
*
*
*
(l) A State must come into substantial
compliance with the requirements of
subpart B of this part and part 383 of
this chapter in effect as of November 27,
2018 as soon as practicable, but, unless
otherwise specifically provided in this
part, not later than November 27, 2021.
Issued under authority delegated in 49 CFR
1.87. September 25, 2018.
Raymond P. Martinez,
Administrator.
[FR Doc. 2018–21289 Filed 9–27–18; 8:45 am]
BILLING CODE 4910–EX–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 223
[Docket No. 160614518–8790–03]
RIN 0648–XE685
Endangered and Threatened Wildlife
and Plants; Final Rule To List the
Chambered Nautilus as Threatened
Under the Endangered Species Act
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
AGENCY:
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Federal Register / Vol. 83, No. 189 / Friday, September 28, 2018 / Rules and Regulations
We, NMFS, announce a final
rule to list the chambered nautilus
(Nautilus pompilius) as threatened
under the Endangered Species Act
(ESA). We have reviewed the status of
the chambered nautilus, including
efforts being made to protect this
species, and considered public
comments, including new information,
submitted on the proposed rule. We
have made our final determination
based on the best scientific and
commercial data available. At this time,
we conclude that critical habitat is not
determinable because data sufficient to
perform the required analyses are
lacking; however, we solicit information
on habitat features and areas in U.S.
waters that may meet the definition of
critical habitat for the chambered
nautilus.
DATES: This final rule is effective
October 29, 2018.
ADDRESSES: Endangered Species
Division, NMFS Office of Protected
Resources (F/PR3), 1315 East West
Highway, Silver Spring, MD 20910.
Copies of the petition, status review
report, and Federal Register notices are
available on our website at https://
www.fisheries.noaa.gov/species/
chambered-nautilus.
FOR FURTHER INFORMATION CONTACT:
Maggie Miller, NMFS, Office of
Protected Resources, (301) 427–8403.
SUPPLEMENTARY INFORMATION:
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SUMMARY:
Background
On May 31, 2016, we received a
petition from the Center for Biological
Diversity to list the chambered nautilus
(N. pompilius) as a threatened species or
an endangered species under the ESA.
We found that the petitioned action may
be warranted for the species and
announced the initiation of a status
review (81 FR 58895, August 26, 2016).
On October 23, 2017, we announced a
positive 12-month finding on the
petition and published a proposed rule
to list the chambered nautilus as a
threatened species under the ESA (82
FR 48948). We solicited information on
the proposed listing determination, the
potential development of proposed
protective regulations, and potential
designation of critical habitat for the
chambered nautilus. The comment
period was open through December 22,
2017, and no hearing requests were
received. This final rule provides an
overview of the ESA listing and status
review process for this species; a
discussion of the comments and
information we received during the
public comment period, as well as our
responses to those comments; a
summary of the statutory listing factors
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and other considerations supporting the
listing determination; and our final ESA
listing determination for the chambered
nautilus. This rule should be read in
conjunction with the proposed rule.
Listing Species Under the Endangered
Species Act
We are responsible for determining
whether species are threatened or
endangered under the ESA (16 U.S.C.
1531 et seq.). To make this
determination, we first consider
whether a group of organisms
constitutes a ‘‘species’’ under section 3
of the ESA, then whether the status of
the species qualifies it for listing as
either threatened or endangered.
Section 3 of the ESA defines
‘‘species’’ to include any subspecies of
fish or wildlife or plants and, for any
vertebrate species, any distinct
population segment (DPS) that
interbreeds when mature (16 U.S.C.
1532(16)). Because the chambered
nautilus is an invertebrate, the ESA does
not permit us to consider listing
populations as DPSs.
Section 3 of the ESA defines an
‘‘endangered species’’ as a species
which is in danger of extinction
throughout all or a significant portion of
its range and a ‘‘threatened species’’ as
one which is likely to become an
endangered species within the
foreseeable future throughout all or a
significant portion of its range. 16 U.S.C.
1532(6); (20). Thus, in the context of the
ESA, we interpret an ‘‘endangered
species’’ to be one that is presently in
danger of extinction. A ‘‘threatened
species’’ 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 and endangered species is
the timing of when a species is or is
likely to become in danger of extinction,
either presently (endangered) or in the
foreseeable future (threatened).
As we explained in the proposed rule
and summarize here, when we consider
whether a species might qualify as
threatened under the ESA, we must
consider the meaning of the term
‘‘foreseeable future.’’ It is appropriate to
interpret ‘‘foreseeable future’’ as the
horizon over which predictions about
the conservation status of the species
can be reasonably relied upon. The
appropriate timescales for analyzing
various threats will vary with the data
available about each threat. The
foreseeable future considers the life
history of the species, habitat
characteristics, availability of data,
particular threats, ability to predict
threats, and the ability to reliably
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48977
forecast the effects of these threats and
future events on the status of the species
under consideration. Because a species
may be susceptible to a variety of threats
for which different data are available, or
which operate across different time
scales, the foreseeable future is not
necessarily reducible to a particular
number of years.
The statute also requires us to
determine whether any species is
endangered or threatened throughout all
or a significant portion of its range as a
result of any one or a combination of the
following factors: The present or
threatened destruction, modification, or
curtailment of its habitat or range;
overutilization for commercial,
recreational, scientific, or educational
purposes; disease or predation; the
inadequacy of existing regulatory
mechanisms to address identified
threats; or other natural or manmade
factors affecting its continued existence
(ESA section 4(a)(1)(A)–(E); 16 U.S.C.
1533(a)(1)(A)–(E). See also 50 CFR
424.11(c)).
To make a listing determination, we
first determine whether a petitioned
species meets the ESA definition of a
‘‘species.’’ Next, using the best available
information gathered during the status
review for the species, we assess the
extinction risk of the species. In
assessing the extinction risk of a
species, in conjunction with the section
4(a)(1) factors, we consider demographic
risk factors, such as those developed by
McElhany et al. (2000), to organize and
evaluate the forms of risks. The
demographic risk analysis is an
assessment of the manifestation of past
threats that have contributed to the
species’ current status and also informs
the consideration of the biological
response of the species to present and
future threats. The approach of
considering demographic risk factors to
help frame the consideration of
extinction risk has been used in many
of our previous status reviews (see
https://www.fisheries.noaa.gov/
resources/documents?title=&field_
category_document_value%5Besa_
status_review%5D=esa_status_
review&species=&field_species_vocab_
target_id=&sort_by=created for links to
these reviews). In this approach, the
collective condition of individual
populations is considered at the species
level according to four demographic
viability factors: Abundance and trends,
population growth rate or productivity,
spatial structure and connectivity, and
genetic diversity. These viability factors
reflect concepts that are well-founded in
conservation biology and that
individually and collectively provide
strong indicators of extinction risk.
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Where a species is found not to
warrant listing throughout its range, we
must go on to evaluate whether the
species may be endangered or
threatened in a ‘‘significant portion of
its range.’’ Conversely, where a species
is found to warrant listing as an
endangered species or a threatened
species based on a review of its status
throughout its range, it is not necessary
to proceed to an evaluation of
potentially significant portions of the
range. As explained more fully in the
proposed rule, we interpret the Act to
require that, where the best available
information allows us to determine a
status for the species rangewide, that
status determination should be given
conclusive weight. Our interpretation is
also consistent with the 2014 Final
Policy on Interpretation of the Phrase
‘‘Significant Portion of its Range’’ (79 FR
37578, July 1, 2014).1
Section 4(b)(1)(A) of the ESA requires
us to make listing determinations based
solely on the best scientific and
commercial data available after
conducting a review of the status of the
species and after taking into account
any efforts being made by any State or
foreign nation or political subdivision
thereof to protect the species. 16 U.S.C.
1533(b)(1)(A). Therefore, prior to
making a listing determination, we also
assess such protective efforts to
determine if they ameliorate the existing
threats to a degree that would affect the
listing status of the species under the
Act. Any relevant foreign efforts are
directly evaluated under standards
deducible from section 4(b)(1)(A) and
the statute’s structure.
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Status Review
A summary of basic biological and life
history information of the chambered
nautilus can be found in the proposed
rule and the status review report. In
reaching our proposed listing
determination, we used the best
available scientific and commercial data
on the chambered nautilus, which are
summarized in the status review report
and incorporated herein.
Scientific conclusions about the
overall risk of extinction faced by the
chambered nautilus under present
1 Although two district courts have held in
litigation involving the United States Fish and
Wildlife Service (USFWS) that the Final Policy’s
specific definition of ‘‘significant’’ is too narrow
(Center for Biological Diversity, et al. v. Jewell, CV–
14–02506 (D. Ariz.); Desert Survivors, et al. v. Dep’t
of Interior, 16-cv-01165 (N.D. Cal.)), all other
provisions of the Final Policy continue in full effect
for both Services, including the provisions
establishing the overall process for sequencing
determinations. Nevertheless, our approach is
reached and applied independently of the Final
Policy.
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conditions and in the foreseeable future
are based on our evaluation of the
species’ demographic risks and ESA
section 4(a)(1) threat factors. Our
assessment of overall extinction risk
considered the likelihood and
contribution of each particular factor,
synergies among contributing factors,
and the cumulative impact of all
demographic risks and threats on the
chambered nautilus. After considering
conservation efforts by foreign nations
to protect the species, as required under
section 4(b)(1)(A), we proposed to list
the species as a ‘‘threatened species.’’
For the assessment of extinction risk
for the chambered nautilus, the
‘‘foreseeable future’’ was considered to
extend out several decades (> 40 years).
Given the species’ life history traits,
with longevity estimated to be at least
20 years, maturity ranges from 10 to 17
years, with very low fecundity
(potentially 10–20 eggs per year with a
1-year incubation period), it would
likely take more than a few decades (i.e.,
multiple generations) for any recent
management actions to be realized and
reflected in population abundance
indices. Similarly, the impact of present
threats to the species could be realized
in the form of noticeable population
declines within this time frame, as
demonstrated in the available survey
and fisheries data. As the main potential
operative threat to the species is
overutilization, this time frame would
allow for reliable predictions regarding
the impact of current levels of fisheryrelated mortality on the biological status
of the species. Additionally, this time
frame allows for consideration of the
previously discussed impacts on
chambered nautilus habitat from climate
change and the potential effects on the
status of this species.
To make our final listing
determination, we reviewed all
comments and information provided
during the public comment period on
the proposed rule. In general, this
additional information merely
supplemented, and did not differ
significantly from, the information
presented in the proposed rule. Where
new information was received, we have
reviewed it and present our evaluation
of the information in this final rule. The
new information received was not so
significant that we are relying on it for
our final determination.
With this rule, we finalize our listing
determination for the chambered
nautilus as a ‘‘threatened species.’’
Summary of Comments
In response to our request for public
comments on the proposed rule, we
received comments and/or relevant
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information from 16 parties. The large
majority of commenters supported the
proposed listing determination but
provided no new or substantive data or
information relevant to the listing of the
chambered nautilus. We also solicited
comments from the countries where the
chambered nautilus occurs via their
ambassadors and received a response
from the Philippines Bureau of Fisheries
and Aquatic Resources and the
Government of India. Summaries of the
substantive public comments received
and our responses are provided below
and organized by topic.
Comments on Available Data, Trends,
and Analysis
Comment 1: Two commenters
provided their personal observations
regarding the decline of the chambered
nautilus in the Indo-Pacific. One
commenter noted that during their 20
years as a researcher studying the
chambered nautilus, 1–2 of their study
sites are now 100 percent depleted and
others are rapidly following suit.
Another commenter provided
information on historical and current
nautilus fishing practices in the
Philippines. The commenter stated that
nautilus fishing was more lucrative in
the 1970s and 1980s in the region of
Central Visayas (particularly the Tan˜on
Strait municipalities) compared to the
end of the 1990s, resulting in reduced
fishing effort of the species. In March
2017, interviews conducted with three
shell exporters on Mactan Islands (the
major export hub for sea shells from
Philippine waters) revealed that they
had a few hundred nautilus shells in
stock (despite the ban on trade in
nautilus shells). The commenter also
stated that there are known locations in
Central Palawan as well as the southern
tip of the island where nautilus fisheries
were or still exist. However, the
commenter noted that it is unclear
whether the nautilus is a target species
or just landed as bycatch. The
commenter stressed the importance of
obtaining information on current and
historical fishing activities in order to
obtain a better understanding of the
present status of nautilus populations in
the Philippines.
Response: We thank the commenters
for the information. We have updated
the status review report (Miller 2018) to
reflect the new information provided
regarding the March 2017 interviews,
which further supports our conclusion
that existing regulations to protect N.
pompilius from overutilization
throughout the Philippines are
inadequate. We agree with the
commenter that fisheries information is
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useful when examining the status of
nautilus populations.
Comment 2: One commenter provided
new published information on the
genetics of the Nautilus genus,
including an estimated effective
population size of N. pompilius across
the Indo-Pacific. Specifically, the
commenter referenced the study by
Combosch et al. (2017), which used
genome-wide double digest restrictionsite associated DNA data to re-analyze
nautiloid species taxonomy. The
commenter noted that the results from
the new study suggest that the
geographic distribution of N. pompilius
may be smaller than previously thought,
and would not include nautilids found
in the Coral Sea and Southwest Pacific.
However, the commenter noted that
further research is needed to validate
the results before a final decision on the
actual geographical range of N.
pompilius is made. In fact, the
commenter stated that given that further
research is still necessary, NMFS should
rely on the best available science and
list N. pompilius as one species (one
‘‘superspecies’’) throughout its range, as
stated in the proposed rule.
In terms of effective population size,
the commenter noted that the estimates
provided in Combosch et al. (2017)
generally tend to be in agreement with
previous genetic studies (i.e., Williams
et al. (2015)). While the estimates are
rather large (for example, ∼4.5 million
specimens of N. pompilius may
potentially exist in the entire IndoPacific), the commenter cautioned that
the data are more than two decades old
and represent what the species could
potentially support based on its current
genetic diversity, not its current living
population abundance estimate. The
commenter cautioned that the
substantial removal of individuals from
N. pompilius populations in recent
decades, and potential losses in genetic
diversity, would take some time before
being reflected in genetic-based effective
population sizes. Ultimately, the
commenter requested that the new
genetic information, discussed above, be
included in the final rule.
Response: We reviewed the paper
referenced by the commenter
(Combosch et al. 2017) and have
updated the status review report with
this new information. Specifically,
Combosch et al. (2017) indicate the
existence of three main Nautilus clades:
South Pacific, Coral Sea, and IndoPacific. The authors contend that these
three clades consist of five distinct
genetic clusters of Nautilus that most
likely correspond to five different
species. Three of these species exist in
the South Pacific, including N.
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macromphalus in New Caledonia and
two undescribed species (one around
American Samoa and Fiji and the other
around Vanuatu). A fourth species is
found from the Great Barrier Reef to
eastern Papua New Guinea, which the
authors consider to be N. stenomphalus.
The fifth species, N. pompilius, occurs
from Western Australia throughout
Indonesia and the Philippines and west
to Palau. The authors also suggest that
N. belauensis and N. repertus should be
synonymized with N. pompilius as they
are both nested within this Indo-Pacific
clade.
While the results from Combosch et
al. (2017) contrast with our
characterization of N. pompilius and its
range within the status review report
and proposed rule, we find that this
new information does not change our
recognition of N. pompilius as a valid
species for listing under the ESA, or our
description of the species and its range
based on the best available information.
As noted in the status review report and
proposed rule, nautilus taxonomy is
controversial and is still not fully
resolved. Until there is a new scientific
agreement regarding the taxonomy of
the Nautilus genus, we will continue to
follow the latest scientific consensus as
acknowledged by the Integrated
Taxonomic Information System, with N.
pompilius identified as one of five
recognized species (N. pompilius, N.
belauensis, N. macromphalus, N.
repertus, and N. stenomphalus). In
terms of range, we find that the best
available information suggest that N.
pompilius is found throughout the IndoPacific and within the South Pacific,
including waters off American Samoa,
Australia, Fiji, India, Indonesia,
Malaysia, New Caledonia, Papua New
Guinea, Philippines, Solomon Islands,
and Vanuatu. Nautilus pompilius is also
possibly native to China, Myanmar,
Western Samoa, Thailand, and Vietnam.
With respect to the new effective
population size estimates in Combosch
et al. (2017), we have updated the status
review report with this data. The
authors estimated median current
effective population sizes for each of the
genetic clades mentioned above (IndoPacific, Coral Sea, South Pacific) and
found large population sizes in the
panmictic Indo-Pacific population (4.5 ×
106 specimens; 3.2 × 106 for the
Philippines subpopulation) and in the
Coral Sea (7.2 × 106 for the Great Barrier
Reef and 5.7 × 106 for Papua New
Guinea). The South Pacific clade had
much smaller effective population sizes,
with New Caledonia at 0.34 × 106
specimens, Vanuatu at 0.67 × 106
specimens, and American Samoa/Fiji
population at 0.41 × 106 specimens. As
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48979
the commenters note, these estimates
are similar to those from previous
genetic studies as reported Williams et
al. (2015). Specifically, Williams et al.
(2015) estimated an effective population
size for the Philippines of 3.2 × 106
individuals, and 2.6 × 106 individuals
for Western Australia. While this new
data further support the suggestion that
the species may have high genetic
diversity, we agree with the commenters
that the current level of genetic diversity
across the entire range of the species
remains highly uncertain. Due to the
low fecundity and long generation time
of the species, genetic responses to
current exploitation rates (such as
decreases in genetic diversity) may not
yet be detectable. We have updated the
status review report with this new data
but do not find that it changes our
conclusions regarding the risk that
genetic diversity currently poses to the
species.
Comments on Existing Regulatory
Mechanisms
Comment 3: The Philippines Bureau
of Fisheries and Aquatic Resources (the
Bureau) provided information regarding
existing regulations. Specifically, the
Bureau stated that under Section 102 (b)
of the Philippine Fisheries Code of 1998
(RA 8550 as amended by RA 10654), it
is unlawful to fish, take, catch, gather,
sell, purchase, possess, transport,
export, forward or ship out aquatic
species listed under Appendix II and III
of the Convention on International
Trade in Endangered Species of Wild
Fauna and Flora (CITES). Based on the
listing of the chambered nautilus in
Appendix II of CITES during the
Conference of the Parties in 2016, the
prohibition became effective on January
2, 2017. However, the export of
government-inventoried chambered
nautilus Pre-Convention specimens
used in the shell craft industry of Cebu,
Philippines is allowed until 2018.
Response: We thank the Bureau for its
comment and have updated the status
review report to reflect this regulation.
However, at this time, we have no
information regarding the effectiveness
of this prohibition, including
subsequent enforcement efforts, in
protecting the chambered nautilus from
continued overutilization throughout
the Philippines. Available information
from the status review report suggests
enforcement of current regulations may
be lacking, with evidence of nautilus
products being sold in shops in Cebu,
the Western Visayas region, and
Palawan as recently as 2017, despite
local ordinances that prohibit the trade
and harvest of N. pompilius. Given the
significant harvest and trade of the
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chambered nautilus throughout the
Philippines (with the Philippines being
the number one supplier of nautilus
commodities to the United States) and
present uncertainty regarding the
enforcement of existing regulatory
measures and subsequent adequacy in
reducing the threat of overutilization to
the species in the foreseeable future, we
find that our conclusions regarding
threats to the species and its extinction
risk remains the same.
Comment 4: The Government of India
(the Government) provided information
on India’s existing regulations related to
the protection of the chambered
nautilus. Specifically, the Government
commented that the chambered nautilus
is listed on Schedule I of India’s Wild
Life (Protection) Act, 1972, which
provides the species with the highest
degree of protection from hunting and
trade. Commercial trade of N. pompilius
in India is not permitted. Additionally,
the Government states that there are no
reports of captures of chambered
nautiluses in Indian fishery landing
centers. However, the Government notes
that illegal trade in the species cannot
be ruled out.
The Government of India also
commented that India, along with Fiji
and the United States, proposed the
listing of Nautilidae on Appendix II of
CITES during the 17th meeting of the
Conference of the Parties to CITES.
Considering this, the Government states
that India has no objections to the
listing of the species as threatened
under the ESA.
Response: We thank the Government
of India for its comment and support of
the listing of chambered nautilus under
the ESA. In the status review report, we
recognized the listing of N. pompilius
under Schedule I of the Indian Wild Life
(Protection) Act of 1972; however, we
found information indicating that N.
pompilius shells were still being
collected in Indian waters and sold in
major coastal tourist curio markets as
recently as 2007 (John et al. 2012). In
fact, interviews with retail vendors
suggested that a large majority were
aware of the Indian Wild Life Protection
Act and legal ramifications of selling
protected species yet continued to sell
large quantities of protected marine
mollusks and corals in the curio shops
(John et al. 2012). Additionally, based
on the shell size of the chambered
nautiluses in the curio shops, we found
it likely that the inventory is comprised
entirely of shells from immature
individuals. While India may prohibit
the harvest and trade of chambered
nautilus, the best available information
suggests that the species is still being
exploited, with the high demand for
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nautilus shells and profits from the
illegal curio trade resulting in the
overutilization of N. pompilius that will
continue to threaten populations within
Indian waters. With no new information
to consider regarding the effectiveness
of enforcement of India’s existing
regulatory mechanisms, we find that our
conclusions regarding threats to the
species and its extinction risk remains
the same.
Comments on Proposed Listing
Determination
Comment 5: We received a number of
comments that supported the proposed
listing of the chambered nautilus as a
threatened species under the ESA. A
large majority of the comments were
general statements of support for listing
and were not accompanied by
substantive information or references.
Some of the comments were
accompanied by information that is
consistent with, or cited directly from,
our proposed rule or status review
report.
Response: Given that no new
substantive information was provided in
these comments that was not already
considered in the proposed rule or
status review report, our conclusion
regarding the status of the chambered
nautilus remains the same. We
acknowledge these comments and the
considerable public interest expressed
in support of the conservation of the
chambered nautilus.
Comment 6: Several commenters
requested that we list the chambered
nautilus as an endangered species under
the ESA. One commenter stated that
listing as endangered is warranted for a
host of reasons including: how little is
known about the biology and ecology of
the chambered nautilus; lack of
information on population abundance
and trends in vast portions of the
species’ range; the species’ reproductive
characteristics (i.e., long-lived, late
maturing, slow growing); its patchy
distribution, geographic isolation,
specialized habitat needs, and genetic
distinction between populations; the
massive level of international trade in
the species (including in to the United
States); and the lack of effective
regulations protecting the species where
it exists. The commenter suggested that
the ‘‘precautionary principle’’ would
indicate that the species should be
listed as an endangered species.
Response: The commenters did not
provide any new information regarding
threats to the species or its current
status that was not already considered
in the status review report or proposed
rule. One commenter cited the proposed
rule and status review report to support
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their argument of listing the chambered
nautilus as, ‘‘preferably,’’ an endangered
species. With no new information to
consider, our conclusion regarding the
status of the chambered nautilus
remains the same.
Regarding the request to use a
precautionary approach when making a
listing decision, it would be
inappropriate apply a presumption in
favor of a particular listing status under
the Act. Under the framework of the
ESA, the threshold determination of
whether or not to list a species is
required to be a scientific conclusion
based solely on the best available
scientific and commercial information.
In carrying out other provisions under
the ESA that come into play after the
time of listing, such as conducting
consultations under section 7, it may be
appropriate to apply a ‘‘precautionary
approach’’ or give the benefit of the
doubt to the species. But such
considerations do not apply at the step
of making a listing determination under
Section 4. Trout Unlimited v. Lohn, 645
F. Supp. 2d 929, 947–48 (D. Or. 2007).
We simply may not list a species as
endangered unless the best available
scientific and commercial information
supports concluding that it meets the
statutory definition of an ‘‘endangered
species’’ at the time of listing.
Comments on Establishing Protective
Regulations Under Section 4(d) of the
ESA
Comment 7: Two commenters urged
us to promulgate a section 4(d) rule to
establish import prohibitions of the
species into the United States and other
trade regulations, as well as to require
permits in order to address the threat of
unsustainable overharvesting of the
species that supports the international
shell trade. As support for their request,
one commenter stated that the CITES
protection for the species will not be
enough to prevent it from becoming
endangered in the foreseeable future
because illegal trade is likely to happen.
Additionally, the commenter noted that
without ESA protections, unregulated
interstate sale (including from American
Samoa) would continue. Thus, even
with the CITES Appendix II listing, the
commenter stated that regulatory
mechanisms remain inadequate to
ensure the species’ survival in the
foreseeable future. The commenters
noted that a 4(d) rule restricting trade,
including import prohibitions, would
allow the U.S. authority to review
CITES non-detriment findings and make
their own determinations as well as
ensure adequate trade restrictions where
domestic efforts to protect the species in
foreign countries have failed.
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Response: Under the ESA, if a species
of fish or wildlife is listed as
endangered, a number of protections set
out in section 9(a)(1) of the Act (16
U.S.C. 1538(a)(1)) automatically apply.
Among other prohibitions, any ‘‘take’’
of, import into or export from the
United States, and interstate or foreign
commerce in the species, is illegal,
subject to certain exceptions. In the case
of a species listed as threatened, the
protections of section 9 do not
automatically apply. However, section
4(d) of the ESA gives the Secretary the
authority to issue such regulations as he
or she deems necessary and advisable to
provide for the conservation of the
species. The Secretary may also prohibit
with respect to a threatened species any
or all of the acts prohibited under
section 9(a)(1) of the ESA. 16 U.S.C.
1533(d).
While the commenter stated that
CITES protection for the species would
not be sufficient to prevent the
chambered nautilus from becoming
endangered in the foreseeable future,
the commenter pointed to no
information regarding current
implementation efforts and enforcement
of CITES requirements, or overall
effectiveness of the CITES Appendix II
listing in ensuring the sustainable trade
of the chambered nautilus to support
their assertion. If sustainable trade in
this species is achieved as a result of the
CITES Appendix II listing, the need for
additional protective measures would
be unnecessary; however, at this time,
we are still evaluating the effectiveness
of the CITES Appendix II listing of the
chambered nautilus. Also, in response
to the commenter’s concerns regarding
interstate commerce, as mentioned in
the proposed rule and status review
report, we found no evidence of local
utilization or commercial harvest of
chambered nautiluses in American
Samoa. Therefore, any sale of nonimported chambered nautilus shells in
interstate commerce would likely
involve collected drift shells from
American Samoa (i.e., the only portion
of the species’ range in U.S. waters). As
such, we do not agree with the
commenter that this interstate
commerce places the species at risk of
extinction at this time.
Summary of Changes From the
Proposed Listing Rule
We did not receive, nor did we find,
data or references that presented
substantial new information that would
cause us to change our proposed listing
determination. We did, however, make
several revisions to the final status
review report (Miller 2018) to
incorporate, as appropriate, relevant
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information received in response to our
request for public comments.
Specifically, we updated the status
review to include new information
regarding the sale of nautilus shells in
the Philippines (K. Schroeder, pers.
comm. 2017), the taxonomy of the
species (Combosch et al. 2017), and
estimates of effective population sizes
for nautilus populations (Combosch et
al. 2017). As noted above, with more
detailed discussion in the previous
comment responses, consideration of
this new information did not alter any
conclusions (and in some cases further
supported our conclusions) regarding
the threat assessment or extinction risk
analysis for the chambered nautilus.
Thus, the conclusion contained in the
status review report and determination
based on that conclusion in the
proposed rule are reaffirmed in this
final action.
Species Determination
As noted previously, nautilus
taxonomy is controversial and still not
fully resolved. However, the current
scientific consensus is that N. pompilius
is a recognized taxonomically-distinct
species and, therefore, meets the
definition of ‘‘species’’ pursuant to
section 3 of the ESA, making it eligible
for listing under the ESA.
Summary of Demographic Risk
Analysis
As stated previously and as discussed
in the proposed rule (82 FR 48948,
October 23, 2017), we conducted a
demographic risk analysis for the
chambered nautilus. This analysis
evaluated the population viability
characteristics and trends data available
for the species to determine the
potential risks these demographic
factors pose to the species. Based on the
available data, we found that the species
exists as small and isolated populations
throughout its range, with low rates of
dispersal and little gene flow among
populations, particularly those that are
separated by large geographic distances
and deep ocean expanses. Genetic
variability within the species has likely
been reduced due to bottleneck events
and genetic drift in the small and
isolated N. pompilius populations
throughout its range. Additionally, the
data indicate that the chambered
nautilus is a slow-growing and latematuring species (with maturity
estimated between 10 and 17 years, and
longevity at least 20 years) with likely
very low productivity and, thus, is
extremely susceptible to decreases in its
abundance. In fact, the data suggest that
many chambered nautilus populations
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48981
are in decline and may be extirpated in
the next several decades.
The comments that we received on
the proposed rule provided information
that was either already considered in
our analysis, was not substantial or
relevant, or was consistent with or
reinforced information in the status
review report and proposed rule.
Therefore, our consideration of the
information received has not altered our
analysis of the demographic risks to the
species.
Summary of ESA Section 4(a)(1)
Factors Affecting the Chambered
Nautilus
As stated previously and as discussed
in the proposed rule (82 FR 48948,
October 23, 2017), we considered
whether any one or a combination of the
five threat factors specified in section
4(a)(1) of the ESA are contributing to the
extinction risk of the chambered
nautilus and result in the species
meeting the definition of ‘‘endangered
species’’ or ‘‘threatened species.’’ The
primary threat to the chambered
nautilus is overutilization through
commercial harvest to meet the demand
for the international nautilus shell trade.
Out of the 10 nations where N.
pompilius is known to occur,
potentially half have targeted nautilus
fisheries either historically or currently.
These waters comprise roughly threequarters of the species’ known range.
Current estimated levels of harvest to
meet the international demand are
projected to lead to extirpations of local
N. pompilius populations as has been
observed in the past. Additionally,
efforts to address overutilization of the
species through regulatory measures
appear inadequate, with evidence of
targeted fishing of and trade in the
species, particularly in Indonesia,
Philippines, and China, despite
prohibitions.
The comments that we received on
the proposed rule provided information
that was either already considered in
our analysis, was not substantial or
relevant, or was consistent with or
reinforced information in the status
review report and proposed rule.
Therefore, our consideration of the
information received has not led us to
change our conclusions regarding any of
the section 4(a)(1) factors or their
interactions. All of the information,
discussion, and conclusions regarding
the factors affecting the chambered
nautilus contained in the final status
review report (Miller 2018) and the
proposed rule is reaffirmed in this final
action.
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Extinction Risk
As discussed previously, the status
review report evaluated the
demographic risks to the chambered
nautilus according to four categories—
abundance and trends, population
growth/productivity, spatial structure/
connectivity, and genetic diversity. As a
concluding step, after considering all of
the available information regarding
demographic and other threats to the
species, we rated the species’ extinction
risk according to a qualitative scale
(high, moderate, and low risk). We
found that N. pompilius is at a moderate
risk of extinction throughout its range.
We explained in the proposed rule that
a species is at a ‘‘moderate risk’’ of
extinction when it is on a trajectory that
puts it at a high level of extinction risk
in the foreseeable future. A species may
be at moderate risk of extinction
because of projected threats or declining
trends in abundance, productivity,
spatial structure, or diversity. While the
chambered nautilus is still traded in
considerable amounts (upwards of
thousands to hundreds of thousands
annually), with evidence of new sites
being established for nautilus fishing
(e.g., in Indonesia, Philippines, Papua
New Guinea), and areas of stable,
unfished populations (e.g., eastern
Australia, American Samoa), we
concluded that without adequate
measures controlling the overutilization
of the species, N. pompilius is on a
trajectory where its overall abundance
will likely see significant declines
within the foreseeable future eventually
reaching the point where the species’
continued persistence will be in
jeopardy. We, therefore, determined that
the species is not presently in danger of
extinction throughout its range but is
likely to become so within the
foreseeable future (i.e., the species is a
threatened species). Because we find
that the chambered nautilus is likely to
become an endangered species within
the foreseeable future throughout its
range, we do not go on to consider
whether the species might be threatened
or endangered in a significant portion of
its range, for the reasons explained in
the Listing Species Under the
Endangered Species Act section above
and more fully in the proposed rule.
The information received from public
comments on the proposed rule was
either already considered in our
analysis, was not substantial or relevant,
or was consistent with or reinforced
information in the status review report
and proposed rule. Therefore, our
consideration of the information
received has not altered our view of the
extinction risk of the chambered
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nautilus. Our conclusion regarding the
extinction risk for the chambered
nautilus remains the same. Therefore,
all of the information, discussion, and
conclusions on the extinction risk of the
chambered nautilus contained in the
final status review report and the
proposed rule is reaffirmed in this final
action.
Protective Efforts
In addition to regulatory mechanisms
(considered under ESA section
4(a)(1)(D)), we considered other efforts
being made to protect the chambered
nautilus (pursuant to ESA section
4(b)(1)(A)). The efforts we evaluated
included a non-profit campaign devoted
to raising the awareness of threats to the
chambered nautilus and the potential
for aquaculture or artificial propagation
programs to satisfy the trade industry
demand for shells and restore wild
populations. We considered whether
such protective efforts sufficiently
ameliorated the identified threats to the
point that they would alter the
conclusions of the extinction risk
analysis for the species so as to possibly
avoid the need to list. None of the
information we received on the
proposed rule affected our conclusions
regarding conservation efforts to protect
the chambered nautilus. Thus, all of the
information, discussion, and
conclusions on the protective efforts for
the chambered nautilus contained in the
final status review report and proposed
rule are reaffirmed in this final action.
Final Determination
We have reviewed the best available
scientific and commercial information,
including the petition, the information
in the final status review report (Miller
2018), the comments of peer reviewers,
and public comments. None of the
information received since publication
of the proposed rule (82 FR 48948,
October 23, 2017) altered our analyses
or conclusions that led to our
determination for the chambered
nautilus. Therefore, the determination
in the proposed rule is reaffirmed in this
final rule and stated below.
Based on the best available scientific
and commercial information, and after
considering efforts being made to
protect N. pompilius, we conclude that
the chambered nautilus is not currently
in danger of extinction throughout its
range but is likely to become so in the
foreseeable future throughout all of its
range from threats of overutilization and
the inadequacy of existing regulatory
mechanisms. Therefore, we have
determined that the chambered nautilus
meets the definition of a ‘‘threatened
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species’’ and list it is as such throughout
its range under the ESA.
Effects of Listing
Conservation measures provided for
species listed as endangered or
threatened under the ESA include
designation of critical habitat, to the
maximum extent prudent and
determinable (16 U.S.C. 1533(a)(3)(A));
development of recovery plans (16
U.S.C. 1533(f)); Federal agency
consultations with NMFS under section
7 of the ESA to ensure their actions are
not likely to jeopardize the species or
result in adverse modification or
destruction of critical habitat, should it
be designated (16 U.S.C. 1536); and, for
endangered species, prohibitions on
taking and certain other activities (16
U.S.C. 1538). Prohibitions on taking, or
other protections, may also be extended
through regulation to threatened
species. (16 U.S.C. 1533(d)). In addition,
recognition of the species’ imperiled
status through listing can indirectly
inform voluntary conservation actions
by Federal and State agencies, foreign
entities, private groups, and individuals.
Protective Measures and Prohibitions
Section 7(a)(2) (16 U.S.C. 1536(a)(2))
of the ESA and NMFS/USFWS
regulations (50 CFR part 402) require
Federal agencies to consult with us to
ensure that activities they authorize,
fund, or carry out are not likely to
jeopardize the continued existence of
listed species or destroy or adversely
modify critical habitat. Our section 7
regulations require the responsible
Federal agency to initiate formal
consultation if a Federal action may
affect a listed species or its critical
habitat (50 CFR 402.14(a)). Examples of
Federal actions that may affect the
chambered nautilus include: Fishery
harvest and management practices,
energy projects, discharge of pollution
from point sources, non-point source
pollution, dredging, mining, piledriving, military activities, toxic waste
and other pollutant disposal, and
shoreline development. This list is not
exhaustive, and the extent to which
consultation is required will depend on
the particular facts of any particular
proposed Federal action.
In the case of threatened species, ESA
section 4(d) gives the Secretary
discretion to issue such regulations as
he or she deems necessary and
advisable for the conservation of the
species. 16 U.S.C. 1533(d). The
Secretary may also decide to extend
some or all the prohibitions of section
9(a)(1) of the ESA (16 U.S.C. 1538(a)(1))
to the species.
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As mentioned in the status review
report and proposed rule, all nautilus
species were included on Appendix II of
CITES in October 2016, with the listing
going into effect in January 2017. Export
of nautilus products, such as shells,
requires CITES permits that ensure the
products were legally acquired and that
the Scientific Authority of the State of
export has advised that such export will
not be detrimental to the survival of that
species (after taking into account factors
such as its population status and trends,
distribution, harvest, and other
biological and ecological elements). In
the proposed rule, this CITES protection
was determined not to have ameliorated
the threats to the threatened chambered
nautilus because the CITES listing had
only recently gone into effect and,
therefore, we lacked information that
would allow us to fully evaluate its
adequacy in decreasing the threat of
overutilization. We are still in the
process of collecting information in
order to evaluate the effectiveness of
this CITES Appendix II listing of the
chambered nautilus as a tool to ensure
the sustainable trade in this species. If
we determine that additional measures
may be necessary to safeguard the
species against future depletion of
populations or potential extinction of
the chambered nautilus, then we may
issue protective regulations under
section 4(d) or extend some or all of the
prohibitions of section 9(a)(1) of the
ESA that automatically apply with
respect to endangered species. However,
at this time, we are not proposing to
apply such prohibitions to the
chambered nautilus. We may consider
potential protective regulations
pursuant to section 4(d) for chambered
nautilus in a future rulemaking.
Critical Habitat
Critical habitat is defined in section 3
of the ESA (16 U.S.C. 1532(5)) as: (1)
The specific areas within the
geographical area occupied by a species,
at the time it is listed, on which are
found those physical or biological
features (a) essential to the conservation
of the species and (b) that may require
special management considerations or
protection; and (2) specific areas outside
the geographical area occupied by a
species at the time it is listed upon a
determination that such areas are
essential for the conservation of the
species. ‘‘Conservation’’ means the use
of all methods and procedures needed
to bring the species to the point at
which listing under the ESA is no
longer necessary (i.e., the point at which
it is ‘‘recovered’’). 16 U.S.C. 1532(3).
Section 4(a)(3)(A) of the ESA (16 U.S.C.
1533(a)(3)(A)) requires that, to the
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maximum extent prudent and
determinable, critical habitat be
designated concurrently with the listing
of a species. Designations of critical
habitat must be based on the best
scientific data available and must take
into consideration the economic,
national security, and other relevant
impacts of specifying any particular area
as critical habitat.
At this time, we find that critical
habitat for the chambered nautilus is not
determinable because data sufficient to
perform the required analyses are
lacking. As stated in the status review
report and proposed rule, while it is
known that chambered nautiluses are
extreme habitat specialists, found in
association with steep-sloped forereefs
with sandy, silty, or muddy-bottomed
substrates, and in depths from around
100 meters to 500 meters, the presence
of these features does not necessarily
indicate the likelihood of chambered
nautilus occurrence. Chambered
nautiluses have a patchy distribution
and, given the difficulty associated with
accessing their habitat and observing the
species for research purposes, very little
is known regarding important aspects of
the species’ life history, such as
reproduction and growth in the wild. As
such, we find that sufficient information
is not currently available to: (1) Identify
the physical and biological features
essential to conservation of the species
at an appropriate level of specificity,
particularly given the uncertainty
regarding habitat features necessary to
support important life history needs and
the irregularity and unpredictability of
chambered nautiluses within areas they
are known to occur, (2) determine the
specific geographical areas that contain
the physical and biological features
essential to conservation of the species,
and (3) assess the impacts of the
designation. Therefore, public input on
features and areas under U.S.
jurisdiction that may meet the definition
of critical habitat for the chambered
nautilus is invited. Additional details
about specific types of information
sought are provided in the Information
Solicited section later in this document.
Input may be sent to the Office of
Protected Resources in Silver Spring,
Maryland (see ADDRESSES). Please note
that we are not required to respond to
any input provided on this matter.
Information Solicited
Because critical habitat is not
currently determinable for the
chambered nautilus, we are not
proposing to designate critical habitat in
this rulemaking. We request interested
persons to submit relevant information
regarding the identification of critical
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habitat of the chambered nautilus,
including specific areas within the
geographical area occupied by the
species that include the physical or
biological features essential to the
conservation of the species and that may
require special management
considerations or protection. Areas
outside the occupied geographical area
should also be identified if such areas
themselves are essential for the
conservation of the species. ESA
implementing regulations at 50 CFR
424.12(g) specify that critical habitat
shall not be designated within foreign
countries or in other areas outside of
U.S. jurisdiction. Therefore, we request
information only on potential areas of
critical habitat within U.S. jurisdiction.
Section 4(b)(2) of the ESA requires the
Secretary to consider the economic
impact, impact on national security, and
any other relevant impact of designating
a particular area as critical habitat.
Section 4(b)(2) also gives the Secretary
discretion to consider excluding from a
critical habitat designation any
particular area where the Secretary finds
that the benefits of exclusion outweigh
the benefits of including the area in the
designation, unless excluding that area
will result in extinction of the species.
To inform our consideration of
potential critical habitat, we also request
information describing the following
with respect to the relevant features or
areas: (1) Activities that may affect the
essential features or threats to the
essential features, or to an area of
potential critical habitat itself; (2)
activities that could be affected by
designating specific areas as critical
habitat; and (3) the positive and
negative economic, national security
and other relevant impacts, including
benefits to the recovery of the species,
likely to result if specific areas are
designated as critical habitat. We seek
information regarding the conservation
benefits of designating areas under U.S.
jurisdiction as critical habitat. In
keeping with the guidance provided by
the Office of Management and Budget
(2000; 2003), we seek information that
would allow the monetization of these
effects to the extent possible, as well as
information on qualitative impacts.
Information submitted may include,
but need not be limited to: (1) Scientific
or commercial publications; (2)
administrative reports, maps or other
graphic materials; and (3) information
received from experts. Information and
data are particularly sought concerning:
(1) Maps and specific information
describing the amount, distribution, and
use type (e.g., foraging, reproduction) of
chambered nautilus habitats, as well as
any additional information on occupied
E:\FR\FM\28SER1.SGM
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48984
Federal Register / Vol. 83, No. 189 / Friday, September 28, 2018 / Rules and Regulations
and unoccupied habitat areas; (2) the
reasons why any habitat should or
should not be included in a designation
of critical habitat under sections 3(5)(A)
and 4(b)(2) of the ESA; (3) information
regarding the benefits of designating
particular areas as critical habitat or of
excluding particular areas; (4) current or
planned activities in the areas that
might be proposed for designation and
their possible impacts; (5) any
foreseeable economic or other potential
impacts resulting from designation, and
in particular, any impacts on small
entities; (6) whether specific
unoccupied areas may be essential to
provide additional habitat areas for the
conservation of the species; and (7)
potential peer reviewers for a proposed
critical habitat designation, including
persons with biological and economic
expertise relevant to the species, region,
and designation of critical habitat. We
solicit information from the public,
other concerned governmental agencies,
the scientific community, industry, or
any other interested party (see
ADDRESSES).
References
A list of all references cited in this
final rule is available at
www.regulations.gov (identified by
docket number NOAA–NMFS–2016–
0098) or available upon request (see
ADDRESSES). The peer review report is
available at: https://www.cio.noaa.gov/
services_programs/prplans/
PRsummaries.html. Additional
information can be found on our
website at https://
www.fisheries.noaa.gov/species/
chambered-nautilus.
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), NMFS has
concluded that ESA listing actions are
not subject to the environmental
assessment requirements of the National
Environmental Policy Act (NEPA). (See
NOAA Administrative Order 216–6A
(2016) and Companion Manual ‘‘Policy
and Procedures for Compliance with the
National Environmental Policy Act and
Related Authorities’’ at 2 (2017).
impose substantial direct ccompliance
costs on state and local governments
(unless required by statute). Neither of
those circumstances is applicable to this
final rule; therefore this action does not
have federalism implications as that
term is defined in E.O. 13132. 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.
Executive Order 12866, Regulatory
Flexibility Act, and Paperwork
Reduction Act
Dated: September 24, 2018.
Samuel D. Rauch, III,
Deputy Assistant Administrator for
Regulatory Programs, National Marine
Fisheries Service.
As noted in the Conference Report on
the 1982 amendments to the ESA,
economic impacts cannot be considered
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.
Executive Order 13771, Reducing
Regulation and Controlling Regulatory
Costs
This rule is not an E.O. 13771
regulatory action because this rule is
exempt from review under E.O. 12866.
Executive Order 13132, Federalism
Classification
National Environmental Policy Act
The 1982 amendments to the ESA, in
section 4(b)(1)(A), restrict the
E.O. 13132 requires agencies to take
into account any federalism impacts of
regulations under development. It
includes specific directives for
consultation in situations where a
regulation will preempt state law or
List of Subjects in 50 CFR Part 223
Endangered and threatened species.
For the reasons set out in the
preamble, 50 CFR part 223 is amended
as follows:
PART 223—THREATENED MARINE
AND ANADROMOUS SPECIES
1. The authority citation for part 223
continues to read as follows:
■
Authority: 16 U.S.C. 1531–1543; subpart B,
§ 223.201–202 also issued under 16 U.S.C.
1361 et seq.; 16 U.S.C. 5503(d) for
§ 223.206(d)(9).
2. In § 223.102, amend the table in
paragraph (e) by adding a subheading
for ‘‘Molluscs’’ after the entry for
‘‘Sturgeon, green’’ under the ‘‘Fishes’’
subheading, and by adding an entry for
‘‘Nautilus, chambered’’ underneath the
‘‘Molluscs’’ table subheading to read as
follows:
■
§ 223.102 Enumeration of threatened
marine and anadromous species.
*
*
*
(e) * * *
*
*
Species 1
Common name
*
Description of listed
entity
Scientific name
*
*
*
Citation(s) for listing
determination(s)
*
Critical habitat
*
ESA rules
*
Molluscs
daltland on DSKBBV9HB2PROD with RULES
Nautilus, chambered .........
*
Nautilus pompilius .............
*
Entire species ............
*
*
[Insert Federal Register
page where the document begins], September 28, 2018.
*
NA
*
1 Species
NA
*
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).
VerDate Sep<11>2014
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Federal Register / Vol. 83, No. 189 / Friday, September 28, 2018 / Rules and Regulations
Specifications that describes the
proposed action and other considered
alternatives. The EA provides an
analysis of the biological, economic, and
social impacts of the proposed measures
and other considered alternatives, a
Regulatory Impact Review, and
economic analysis. Copies of the
Framework 5 and 2018–2019
Specifications EA are available on
request from Thomas A. Nies, Executive
Director, New England Fishery
Management Council, 50 Water Street,
Newburyport, MA 01950. This
document is also available from the
following internet addresses: https://
www.nefmc.org and
www.regulations.gov/
#!docketDetail;D=NOAA-NMFS-20180054.
FOR FURTHER INFORMATION CONTACT:
Debra Lambert, Fishery Policy Analyst,
(301) 427–8560.
SUPPLEMENTARY INFORMATION:
[FR Doc. 2018–21114 Filed 9–27–18; 8:45 am]
BILLING CODE 3510–22–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 648
[Docket No. 180130101–8824–02]
RIN 0648–BH57
Fisheries of the Northeastern United
States; Northeast Skate Complex;
Framework Adjustment 5 and 2018–
2019 Specifications
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
AGENCY:
NMFS approves regulations to
implement Northeast Skate Complex
Fishery Management Plan Framework
Adjustment 5 management measures
and 2018–2019 specifications for the
skate fishery. The action is necessary to
establish skate specifications to be
consistent with the most recent
scientific information and improve
management of the skate fisheries. This
action is intended to establish
appropriate catch limits for the skate
fishery and to provide additional
operational flexibility to fishery
participants.
SUMMARY:
Effective on September 28, 2018.
ADDRESSES: New England Fishery
Management Council staff prepared an
environmental assessment (EA) for
Northeast Skate Complex Framework
Adjustment 5 and 2018–2019
DATES:
Background
The Northeast Skate Complex Fishery
Management Plan (FMP), developed by
the New England Fishery Management
Council and implemented in 2003,
manages a complex of seven skate
species (barndoor, clearnose, little,
rosette, smooth, thorny, and winter
skate) off the New England and midAtlantic coasts. Skates are harvested and
managed in two different fisheries: One
for food (the wing fishery) and one for
lobster and crab bait (the bait fishery).
Additional information on the skate
fisheries can be found online at https://
www.greateratlantic.fisheries.noaa.gov/
sustainable/species/skate/.
On July 5, 2018, we proposed
management modifications to
implement Framework Adjustment 5 to
the Northeast Skate Complex FMP and
48985
specifications for fishing years 2018–
2019 (83 FR 31354). After reviewing
public comments in response to the
proposed rule, we are approving
Framework 5 and 2018–2019
specifications as detailed in our
proposed rule.
Specifications for Fishing Years 2018–
2019
Specifications including the
acceptable biological catch (ABC),
annual catch limit (ACL), annual catch
target (ACT), total allowable landings
(TAL) for the skate wing and bait
fisheries, and possession limits may be
specified for up to 2 years. We are
approving the Council’s recommended
specifications for 2018–2019. As
recommended, the 2018–2019 skate
complex ABC and ACL is 31,327 mt.
The ACT is set at 23,495 mt (75 percent
of the ACL) to account for management
uncertainty. After deducting projected
dead discards and state landings, the
overall TAL is 13,157 mt. Tables 1 and
2 (below) detail TALs and possession
limits for the skate wing and skate bait
fisheries. The skate wing and whole
skate possession limits are status quo
and the possession limits for barndoor
skate are described further below.
TABLE 1—TOTAL ALLOWABLE LANDINGS FOR FISHING YEARS 2018–
2019
Total allowable landings (TAL)
Skate Wing Fishery:
Season 1 (May 1–August 31) .........
Season 2 (September 1–April 30) ..
Skate Bait Fishery:
Season 1 (May 1–July 31) ..............
Season 2 (August 1–October 31) ...
Season 3 (November 1–April 30) ...
mt
4,987
3,762
1,358
1,635
1,415
TABLE 2—POSSESSION LIMITS PER TRIP FOR FISHING YEARS 2018–2019
Trip limits
daltland on DSKBBV9HB2PROD with RULES
Skate possession limits *
NE Multispecies, Scallop, or Monkfish DayAt-Sea (DAS):
Season 1 (May 1–August 31) ...............
Season 2 (September 1–April 30) ........
NE Multispecies B DAS:
May 1–April 30 ......................................
Non-DAS:
May 1–April 30 ......................................
Whole skate with bait Letter of Authorization:
May 1–October 31 ................................
November 1–April 30 ............................
Whole skates
Barndoor ** skate wings
2,600 lb, 1,179 kg .....
4,100 lb, 1,860 kg .....
5,902 lb, 2,677 kg .....
9,307 lb, 4,222 kg .....
650 lb, 295 kg ..................
1,025 lb, 465 kg ...............
1,476 lb, 670 kg.
2,327 lb, 1,056 kg.
220 lb, 100 kg ...........
500 lb, 227 kg ...........
0 .......................................
0.
500 lb, 227 kg ...........
1,135 lb, 515 kg ........
0 .......................................
0.
0 ................................
0 ................................
25,000 lb, 11,340 kg
12,000 lb, 5,443 kg ...
0 .......................................
0 .......................................
0.
0.
* Possession limits may be modified in-season in order to prevent catch from exceeding quotas.
** Barndoor skate trip limits are within the overall skate possession limit for each trip, not in addition to it.
VerDate Sep<11>2014
17:35 Sep 27, 2018
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Whole barndoor **
skates
Skate wings
PO 00000
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E:\FR\FM\28SER1.SGM
28SER1
Agencies
[Federal Register Volume 83, Number 189 (Friday, September 28, 2018)]
[Rules and Regulations]
[Pages 48976-48985]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2018-21114]
=======================================================================
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 223
[Docket No. 160614518-8790-03]
RIN 0648-XE685
Endangered and Threatened Wildlife and Plants; Final Rule To List
the Chambered Nautilus as Threatened Under the Endangered Species Act
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Final rule.
-----------------------------------------------------------------------
[[Page 48977]]
SUMMARY: We, NMFS, announce a final rule to list the chambered nautilus
(Nautilus pompilius) as threatened under the Endangered Species Act
(ESA). We have reviewed the status of the chambered nautilus, including
efforts being made to protect this species, and considered public
comments, including new information, submitted on the proposed rule. We
have made our final determination based on the best scientific and
commercial data available. At this time, we conclude that critical
habitat is not determinable because data sufficient to perform the
required analyses are lacking; however, we solicit information on
habitat features and areas in U.S. waters that may meet the definition
of critical habitat for the chambered nautilus.
DATES: This final rule is effective October 29, 2018.
ADDRESSES: Endangered Species Division, NMFS Office of Protected
Resources (F/PR3), 1315 East West Highway, Silver Spring, MD 20910.
Copies of the petition, status review report, and Federal Register
notices are available on our website at https://www.fisheries.noaa.gov/species/chambered-nautilus.
FOR FURTHER INFORMATION CONTACT: Maggie Miller, NMFS, Office of
Protected Resources, (301) 427-8403.
SUPPLEMENTARY INFORMATION:
Background
On May 31, 2016, we received a petition from the Center for
Biological Diversity to list the chambered nautilus (N. pompilius) as a
threatened species or an endangered species under the ESA. We found
that the petitioned action may be warranted for the species and
announced the initiation of a status review (81 FR 58895, August 26,
2016). On October 23, 2017, we announced a positive 12-month finding on
the petition and published a proposed rule to list the chambered
nautilus as a threatened species under the ESA (82 FR 48948). We
solicited information on the proposed listing determination, the
potential development of proposed protective regulations, and potential
designation of critical habitat for the chambered nautilus. The comment
period was open through December 22, 2017, and no hearing requests were
received. This final rule provides an overview of the ESA listing and
status review process for this species; a discussion of the comments
and information we received during the public comment period, as well
as our responses to those comments; a summary of the statutory listing
factors and other considerations supporting the listing determination;
and our final ESA listing determination for the chambered nautilus.
This rule should be read in conjunction with the proposed rule.
Listing Species Under the Endangered Species Act
We are responsible for determining whether species are threatened
or endangered under the ESA (16 U.S.C. 1531 et seq.). To make this
determination, we first consider whether a group of organisms
constitutes a ``species'' under section 3 of the ESA, then whether the
status of the species qualifies it for listing as either threatened or
endangered.
Section 3 of the ESA defines ``species'' to include any subspecies
of fish or wildlife or plants and, for any vertebrate species, any
distinct population segment (DPS) that interbreeds when mature (16
U.S.C. 1532(16)). Because the chambered nautilus is an invertebrate,
the ESA does not permit us to consider listing populations as DPSs.
Section 3 of the ESA defines an ``endangered species'' as a species
which is in danger of extinction throughout all or a significant
portion of its range and a ``threatened species'' as one which is
likely to become an endangered species within the foreseeable future
throughout all or a significant portion of its range. 16 U.S.C.
1532(6); (20). Thus, in the context of the ESA, we interpret an
``endangered species'' to be one that is presently in danger of
extinction. A ``threatened species'' 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 and endangered species is the timing of when a
species is or is likely to become in danger of extinction, either
presently (endangered) or in the foreseeable future (threatened).
As we explained in the proposed rule and summarize here, when we
consider whether a species might qualify as threatened under the ESA,
we must consider the meaning of the term ``foreseeable future.'' It is
appropriate to interpret ``foreseeable future'' as the horizon over
which predictions about the conservation status of the species can be
reasonably relied upon. The appropriate timescales for analyzing
various threats will vary with the data available about each threat.
The foreseeable future considers the life history of the species,
habitat characteristics, availability of data, particular threats,
ability to predict threats, and the ability to reliably forecast the
effects of these threats and future events on the status of the species
under consideration. Because a species may be susceptible to a variety
of threats for which different data are available, or which operate
across different time scales, the foreseeable future is not necessarily
reducible to a particular number of years.
The statute also requires us to determine whether any species is
endangered or threatened throughout all or a significant portion of its
range as a result of any one or a combination of the following factors:
The present or threatened destruction, modification, or curtailment of
its habitat or range; overutilization for commercial, recreational,
scientific, or educational purposes; disease or predation; the
inadequacy of existing regulatory mechanisms to address identified
threats; or other natural or manmade factors affecting its continued
existence (ESA section 4(a)(1)(A)-(E); 16 U.S.C. 1533(a)(1)(A)-(E). See
also 50 CFR 424.11(c)).
To make a listing determination, we first determine whether a
petitioned species meets the ESA definition of a ``species.'' Next,
using the best available information gathered during the status review
for the species, we assess the extinction risk of the species. In
assessing the extinction risk of a species, in conjunction with the
section 4(a)(1) factors, we consider demographic risk factors, such as
those developed by McElhany et al. (2000), to organize and evaluate the
forms of risks. The demographic risk analysis is an assessment of the
manifestation of past threats that have contributed to the species'
current status and also informs the consideration of the biological
response of the species to present and future threats. The approach of
considering demographic risk factors to help frame the consideration of
extinction risk has been used in many of our previous status reviews
(see https://www.fisheries.noaa.gov/resources/documents?title=&field_category_document_value%5Besa_status_review%5D=esa_status_review&species=&field_species_vocab_target_id=&sort_by=created
for links to these reviews). In this approach, the collective condition
of individual populations is considered at the species level according
to four demographic viability factors: Abundance and trends, population
growth rate or productivity, spatial structure and connectivity, and
genetic diversity. These viability factors reflect concepts that are
well-founded in conservation biology and that individually and
collectively provide strong indicators of extinction risk.
[[Page 48978]]
Where a species is found not to warrant listing throughout its
range, we must go on to evaluate whether the species may be endangered
or threatened in a ``significant portion of its range.'' Conversely,
where a species is found to warrant listing as an endangered species or
a threatened species based on a review of its status throughout its
range, it is not necessary to proceed to an evaluation of potentially
significant portions of the range. As explained more fully in the
proposed rule, we interpret the Act to require that, where the best
available information allows us to determine a status for the species
rangewide, that status determination should be given conclusive weight.
Our interpretation is also consistent with the 2014 Final Policy on
Interpretation of the Phrase ``Significant Portion of its Range'' (79
FR 37578, July 1, 2014).\1\
---------------------------------------------------------------------------
\1\ Although two district courts have held in litigation
involving the United States Fish and Wildlife Service (USFWS) that
the Final Policy's specific definition of ``significant'' is too
narrow (Center for Biological Diversity, et al. v. Jewell, CV-14-
02506 (D. Ariz.); Desert Survivors, et al. v. Dep't of Interior, 16-
cv-01165 (N.D. Cal.)), all other provisions of the Final Policy
continue in full effect for both Services, including the provisions
establishing the overall process for sequencing determinations.
Nevertheless, our approach is reached and applied independently of
the Final Policy.
---------------------------------------------------------------------------
Section 4(b)(1)(A) of the ESA requires us to make listing
determinations based solely on the best scientific and commercial data
available after conducting a review of the status of the species and
after taking into account any efforts being made by any State or
foreign nation or political subdivision thereof to protect the species.
16 U.S.C. 1533(b)(1)(A). Therefore, prior to making a listing
determination, we also assess such protective efforts to determine if
they ameliorate the existing threats to a degree that would affect the
listing status of the species under the Act. Any relevant foreign
efforts are directly evaluated under standards deducible from section
4(b)(1)(A) and the statute's structure.
Status Review
A summary of basic biological and life history information of the
chambered nautilus can be found in the proposed rule and the status
review report. In reaching our proposed listing determination, we used
the best available scientific and commercial data on the chambered
nautilus, which are summarized in the status review report and
incorporated herein.
Scientific conclusions about the overall risk of extinction faced
by the chambered nautilus under present conditions and in the
foreseeable future are based on our evaluation of the species'
demographic risks and ESA section 4(a)(1) threat factors. Our
assessment of overall extinction risk considered the likelihood and
contribution of each particular factor, synergies among contributing
factors, and the cumulative impact of all demographic risks and threats
on the chambered nautilus. After considering conservation efforts by
foreign nations to protect the species, as required under section
4(b)(1)(A), we proposed to list the species as a ``threatened
species.''
For the assessment of extinction risk for the chambered nautilus,
the ``foreseeable future'' was considered to extend out several decades
(> 40 years). Given the species' life history traits, with longevity
estimated to be at least 20 years, maturity ranges from 10 to 17 years,
with very low fecundity (potentially 10-20 eggs per year with a 1-year
incubation period), it would likely take more than a few decades (i.e.,
multiple generations) for any recent management actions to be realized
and reflected in population abundance indices. Similarly, the impact of
present threats to the species could be realized in the form of
noticeable population declines within this time frame, as demonstrated
in the available survey and fisheries data. As the main potential
operative threat to the species is overutilization, this time frame
would allow for reliable predictions regarding the impact of current
levels of fishery-related mortality on the biological status of the
species. Additionally, this time frame allows for consideration of the
previously discussed impacts on chambered nautilus habitat from climate
change and the potential effects on the status of this species.
To make our final listing determination, we reviewed all comments
and information provided during the public comment period on the
proposed rule. In general, this additional information merely
supplemented, and did not differ significantly from, the information
presented in the proposed rule. Where new information was received, we
have reviewed it and present our evaluation of the information in this
final rule. The new information received was not so significant that we
are relying on it for our final determination.
With this rule, we finalize our listing determination for the
chambered nautilus as a ``threatened species.''
Summary of Comments
In response to our request for public comments on the proposed
rule, we received comments and/or relevant information from 16 parties.
The large majority of commenters supported the proposed listing
determination but provided no new or substantive data or information
relevant to the listing of the chambered nautilus. We also solicited
comments from the countries where the chambered nautilus occurs via
their ambassadors and received a response from the Philippines Bureau
of Fisheries and Aquatic Resources and the Government of India.
Summaries of the substantive public comments received and our responses
are provided below and organized by topic.
Comments on Available Data, Trends, and Analysis
Comment 1: Two commenters provided their personal observations
regarding the decline of the chambered nautilus in the Indo-Pacific.
One commenter noted that during their 20 years as a researcher studying
the chambered nautilus, 1-2 of their study sites are now 100 percent
depleted and others are rapidly following suit. Another commenter
provided information on historical and current nautilus fishing
practices in the Philippines. The commenter stated that nautilus
fishing was more lucrative in the 1970s and 1980s in the region of
Central Visayas (particularly the Ta[ntilde]on Strait municipalities)
compared to the end of the 1990s, resulting in reduced fishing effort
of the species. In March 2017, interviews conducted with three shell
exporters on Mactan Islands (the major export hub for sea shells from
Philippine waters) revealed that they had a few hundred nautilus shells
in stock (despite the ban on trade in nautilus shells). The commenter
also stated that there are known locations in Central Palawan as well
as the southern tip of the island where nautilus fisheries were or
still exist. However, the commenter noted that it is unclear whether
the nautilus is a target species or just landed as bycatch. The
commenter stressed the importance of obtaining information on current
and historical fishing activities in order to obtain a better
understanding of the present status of nautilus populations in the
Philippines.
Response: We thank the commenters for the information. We have
updated the status review report (Miller 2018) to reflect the new
information provided regarding the March 2017 interviews, which further
supports our conclusion that existing regulations to protect N.
pompilius from overutilization throughout the Philippines are
inadequate. We agree with the commenter that fisheries information is
[[Page 48979]]
useful when examining the status of nautilus populations.
Comment 2: One commenter provided new published information on the
genetics of the Nautilus genus, including an estimated effective
population size of N. pompilius across the Indo-Pacific. Specifically,
the commenter referenced the study by Combosch et al. (2017), which
used genome-wide double digest restriction-site associated DNA data to
re-analyze nautiloid species taxonomy. The commenter noted that the
results from the new study suggest that the geographic distribution of
N. pompilius may be smaller than previously thought, and would not
include nautilids found in the Coral Sea and Southwest Pacific.
However, the commenter noted that further research is needed to
validate the results before a final decision on the actual geographical
range of N. pompilius is made. In fact, the commenter stated that given
that further research is still necessary, NMFS should rely on the best
available science and list N. pompilius as one species (one
``superspecies'') throughout its range, as stated in the proposed rule.
In terms of effective population size, the commenter noted that the
estimates provided in Combosch et al. (2017) generally tend to be in
agreement with previous genetic studies (i.e., Williams et al. (2015)).
While the estimates are rather large (for example, ~4.5 million
specimens of N. pompilius may potentially exist in the entire Indo-
Pacific), the commenter cautioned that the data are more than two
decades old and represent what the species could potentially support
based on its current genetic diversity, not its current living
population abundance estimate. The commenter cautioned that the
substantial removal of individuals from N. pompilius populations in
recent decades, and potential losses in genetic diversity, would take
some time before being reflected in genetic-based effective population
sizes. Ultimately, the commenter requested that the new genetic
information, discussed above, be included in the final rule.
Response: We reviewed the paper referenced by the commenter
(Combosch et al. 2017) and have updated the status review report with
this new information. Specifically, Combosch et al. (2017) indicate the
existence of three main Nautilus clades: South Pacific, Coral Sea, and
Indo-Pacific. The authors contend that these three clades consist of
five distinct genetic clusters of Nautilus that most likely correspond
to five different species. Three of these species exist in the South
Pacific, including N. macromphalus in New Caledonia and two undescribed
species (one around American Samoa and Fiji and the other around
Vanuatu). A fourth species is found from the Great Barrier Reef to
eastern Papua New Guinea, which the authors consider to be N.
stenomphalus. The fifth species, N. pompilius, occurs from Western
Australia throughout Indonesia and the Philippines and west to Palau.
The authors also suggest that N. belauensis and N. repertus should be
synonymized with N. pompilius as they are both nested within this Indo-
Pacific clade.
While the results from Combosch et al. (2017) contrast with our
characterization of N. pompilius and its range within the status review
report and proposed rule, we find that this new information does not
change our recognition of N. pompilius as a valid species for listing
under the ESA, or our description of the species and its range based on
the best available information. As noted in the status review report
and proposed rule, nautilus taxonomy is controversial and is still not
fully resolved. Until there is a new scientific agreement regarding the
taxonomy of the Nautilus genus, we will continue to follow the latest
scientific consensus as acknowledged by the Integrated Taxonomic
Information System, with N. pompilius identified as one of five
recognized species (N. pompilius, N. belauensis, N. macromphalus, N.
repertus, and N. stenomphalus). In terms of range, we find that the
best available information suggest that N. pompilius is found
throughout the Indo-Pacific and within the South Pacific, including
waters off American Samoa, Australia, Fiji, India, Indonesia, Malaysia,
New Caledonia, Papua New Guinea, Philippines, Solomon Islands, and
Vanuatu. Nautilus pompilius is also possibly native to China, Myanmar,
Western Samoa, Thailand, and Vietnam.
With respect to the new effective population size estimates in
Combosch et al. (2017), we have updated the status review report with
this data. The authors estimated median current effective population
sizes for each of the genetic clades mentioned above (Indo-Pacific,
Coral Sea, South Pacific) and found large population sizes in the
panmictic Indo-Pacific population (4.5 x 10\6\ specimens; 3.2 x 10\6\
for the Philippines subpopulation) and in the Coral Sea (7.2 x 10\6\
for the Great Barrier Reef and 5.7 x 10\6\ for Papua New Guinea). The
South Pacific clade had much smaller effective population sizes, with
New Caledonia at 0.34 x 10\6\ specimens, Vanuatu at 0.67 x 10\6\
specimens, and American Samoa/Fiji population at 0.41 x 10\6\
specimens. As the commenters note, these estimates are similar to those
from previous genetic studies as reported Williams et al. (2015).
Specifically, Williams et al. (2015) estimated an effective population
size for the Philippines of 3.2 x 10\6\ individuals, and 2.6 x 10\6\
individuals for Western Australia. While this new data further support
the suggestion that the species may have high genetic diversity, we
agree with the commenters that the current level of genetic diversity
across the entire range of the species remains highly uncertain. Due to
the low fecundity and long generation time of the species, genetic
responses to current exploitation rates (such as decreases in genetic
diversity) may not yet be detectable. We have updated the status review
report with this new data but do not find that it changes our
conclusions regarding the risk that genetic diversity currently poses
to the species.
Comments on Existing Regulatory Mechanisms
Comment 3: The Philippines Bureau of Fisheries and Aquatic
Resources (the Bureau) provided information regarding existing
regulations. Specifically, the Bureau stated that under Section 102 (b)
of the Philippine Fisheries Code of 1998 (RA 8550 as amended by RA
10654), it is unlawful to fish, take, catch, gather, sell, purchase,
possess, transport, export, forward or ship out aquatic species listed
under Appendix II and III of the Convention on International Trade in
Endangered Species of Wild Fauna and Flora (CITES). Based on the
listing of the chambered nautilus in Appendix II of CITES during the
Conference of the Parties in 2016, the prohibition became effective on
January 2, 2017. However, the export of government-inventoried
chambered nautilus Pre-Convention specimens used in the shell craft
industry of Cebu, Philippines is allowed until 2018.
Response: We thank the Bureau for its comment and have updated the
status review report to reflect this regulation. However, at this time,
we have no information regarding the effectiveness of this prohibition,
including subsequent enforcement efforts, in protecting the chambered
nautilus from continued overutilization throughout the Philippines.
Available information from the status review report suggests
enforcement of current regulations may be lacking, with evidence of
nautilus products being sold in shops in Cebu, the Western Visayas
region, and Palawan as recently as 2017, despite local ordinances that
prohibit the trade and harvest of N. pompilius. Given the significant
harvest and trade of the
[[Page 48980]]
chambered nautilus throughout the Philippines (with the Philippines
being the number one supplier of nautilus commodities to the United
States) and present uncertainty regarding the enforcement of existing
regulatory measures and subsequent adequacy in reducing the threat of
overutilization to the species in the foreseeable future, we find that
our conclusions regarding threats to the species and its extinction
risk remains the same.
Comment 4: The Government of India (the Government) provided
information on India's existing regulations related to the protection
of the chambered nautilus. Specifically, the Government commented that
the chambered nautilus is listed on Schedule I of India's Wild Life
(Protection) Act, 1972, which provides the species with the highest
degree of protection from hunting and trade. Commercial trade of N.
pompilius in India is not permitted. Additionally, the Government
states that there are no reports of captures of chambered nautiluses in
Indian fishery landing centers. However, the Government notes that
illegal trade in the species cannot be ruled out.
The Government of India also commented that India, along with Fiji
and the United States, proposed the listing of Nautilidae on Appendix
II of CITES during the 17th meeting of the Conference of the Parties to
CITES. Considering this, the Government states that India has no
objections to the listing of the species as threatened under the ESA.
Response: We thank the Government of India for its comment and
support of the listing of chambered nautilus under the ESA. In the
status review report, we recognized the listing of N. pompilius under
Schedule I of the Indian Wild Life (Protection) Act of 1972; however,
we found information indicating that N. pompilius shells were still
being collected in Indian waters and sold in major coastal tourist
curio markets as recently as 2007 (John et al. 2012). In fact,
interviews with retail vendors suggested that a large majority were
aware of the Indian Wild Life Protection Act and legal ramifications of
selling protected species yet continued to sell large quantities of
protected marine mollusks and corals in the curio shops (John et al.
2012). Additionally, based on the shell size of the chambered
nautiluses in the curio shops, we found it likely that the inventory is
comprised entirely of shells from immature individuals. While India may
prohibit the harvest and trade of chambered nautilus, the best
available information suggests that the species is still being
exploited, with the high demand for nautilus shells and profits from
the illegal curio trade resulting in the overutilization of N.
pompilius that will continue to threaten populations within Indian
waters. With no new information to consider regarding the effectiveness
of enforcement of India's existing regulatory mechanisms, we find that
our conclusions regarding threats to the species and its extinction
risk remains the same.
Comments on Proposed Listing Determination
Comment 5: We received a number of comments that supported the
proposed listing of the chambered nautilus as a threatened species
under the ESA. A large majority of the comments were general statements
of support for listing and were not accompanied by substantive
information or references. Some of the comments were accompanied by
information that is consistent with, or cited directly from, our
proposed rule or status review report.
Response: Given that no new substantive information was provided in
these comments that was not already considered in the proposed rule or
status review report, our conclusion regarding the status of the
chambered nautilus remains the same. We acknowledge these comments and
the considerable public interest expressed in support of the
conservation of the chambered nautilus.
Comment 6: Several commenters requested that we list the chambered
nautilus as an endangered species under the ESA. One commenter stated
that listing as endangered is warranted for a host of reasons
including: how little is known about the biology and ecology of the
chambered nautilus; lack of information on population abundance and
trends in vast portions of the species' range; the species'
reproductive characteristics (i.e., long-lived, late maturing, slow
growing); its patchy distribution, geographic isolation, specialized
habitat needs, and genetic distinction between populations; the massive
level of international trade in the species (including in to the United
States); and the lack of effective regulations protecting the species
where it exists. The commenter suggested that the ``precautionary
principle'' would indicate that the species should be listed as an
endangered species.
Response: The commenters did not provide any new information
regarding threats to the species or its current status that was not
already considered in the status review report or proposed rule. One
commenter cited the proposed rule and status review report to support
their argument of listing the chambered nautilus as, ``preferably,'' an
endangered species. With no new information to consider, our conclusion
regarding the status of the chambered nautilus remains the same.
Regarding the request to use a precautionary approach when making a
listing decision, it would be inappropriate apply a presumption in
favor of a particular listing status under the Act. Under the framework
of the ESA, the threshold determination of whether or not to list a
species is required to be a scientific conclusion based solely on the
best available scientific and commercial information. In carrying out
other provisions under the ESA that come into play after the time of
listing, such as conducting consultations under section 7, it may be
appropriate to apply a ``precautionary approach'' or give the benefit
of the doubt to the species. But such considerations do not apply at
the step of making a listing determination under Section 4. Trout
Unlimited v. Lohn, 645 F. Supp. 2d 929, 947-48 (D. Or. 2007). We simply
may not list a species as endangered unless the best available
scientific and commercial information supports concluding that it meets
the statutory definition of an ``endangered species'' at the time of
listing.
Comments on Establishing Protective Regulations Under Section 4(d) of
the ESA
Comment 7: Two commenters urged us to promulgate a section 4(d)
rule to establish import prohibitions of the species into the United
States and other trade regulations, as well as to require permits in
order to address the threat of unsustainable overharvesting of the
species that supports the international shell trade. As support for
their request, one commenter stated that the CITES protection for the
species will not be enough to prevent it from becoming endangered in
the foreseeable future because illegal trade is likely to happen.
Additionally, the commenter noted that without ESA protections,
unregulated interstate sale (including from American Samoa) would
continue. Thus, even with the CITES Appendix II listing, the commenter
stated that regulatory mechanisms remain inadequate to ensure the
species' survival in the foreseeable future. The commenters noted that
a 4(d) rule restricting trade, including import prohibitions, would
allow the U.S. authority to review CITES non-detriment findings and
make their own determinations as well as ensure adequate trade
restrictions where domestic efforts to protect the species in foreign
countries have failed.
[[Page 48981]]
Response: Under the ESA, if a species of fish or wildlife is listed
as endangered, a number of protections set out in section 9(a)(1) of
the Act (16 U.S.C. 1538(a)(1)) automatically apply. Among other
prohibitions, any ``take'' of, import into or export from the United
States, and interstate or foreign commerce in the species, is illegal,
subject to certain exceptions. In the case of a species listed as
threatened, the protections of section 9 do not automatically apply.
However, section 4(d) of the ESA gives the Secretary the authority to
issue such regulations as he or she deems necessary and advisable to
provide for the conservation of the species. The Secretary may also
prohibit with respect to a threatened species any or all of the acts
prohibited under section 9(a)(1) of the ESA. 16 U.S.C. 1533(d).
While the commenter stated that CITES protection for the species
would not be sufficient to prevent the chambered nautilus from becoming
endangered in the foreseeable future, the commenter pointed to no
information regarding current implementation efforts and enforcement of
CITES requirements, or overall effectiveness of the CITES Appendix II
listing in ensuring the sustainable trade of the chambered nautilus to
support their assertion. If sustainable trade in this species is
achieved as a result of the CITES Appendix II listing, the need for
additional protective measures would be unnecessary; however, at this
time, we are still evaluating the effectiveness of the CITES Appendix
II listing of the chambered nautilus. Also, in response to the
commenter's concerns regarding interstate commerce, as mentioned in the
proposed rule and status review report, we found no evidence of local
utilization or commercial harvest of chambered nautiluses in American
Samoa. Therefore, any sale of non-imported chambered nautilus shells in
interstate commerce would likely involve collected drift shells from
American Samoa (i.e., the only portion of the species' range in U.S.
waters). As such, we do not agree with the commenter that this
interstate commerce places the species at risk of extinction at this
time.
Summary of Changes From the Proposed Listing Rule
We did not receive, nor did we find, data or references that
presented substantial new information that would cause us to change our
proposed listing determination. We did, however, make several revisions
to the final status review report (Miller 2018) to incorporate, as
appropriate, relevant information received in response to our request
for public comments.
Specifically, we updated the status review to include new
information regarding the sale of nautilus shells in the Philippines
(K. Schroeder, pers. comm. 2017), the taxonomy of the species (Combosch
et al. 2017), and estimates of effective population sizes for nautilus
populations (Combosch et al. 2017). As noted above, with more detailed
discussion in the previous comment responses, consideration of this new
information did not alter any conclusions (and in some cases further
supported our conclusions) regarding the threat assessment or
extinction risk analysis for the chambered nautilus. Thus, the
conclusion contained in the status review report and determination
based on that conclusion in the proposed rule are reaffirmed in this
final action.
Species Determination
As noted previously, nautilus taxonomy is controversial and still
not fully resolved. However, the current scientific consensus is that
N. pompilius is a recognized taxonomically-distinct species and,
therefore, meets the definition of ``species'' pursuant to section 3 of
the ESA, making it eligible for listing under the ESA.
Summary of Demographic Risk Analysis
As stated previously and as discussed in the proposed rule (82 FR
48948, October 23, 2017), we conducted a demographic risk analysis for
the chambered nautilus. This analysis evaluated the population
viability characteristics and trends data available for the species to
determine the potential risks these demographic factors pose to the
species. Based on the available data, we found that the species exists
as small and isolated populations throughout its range, with low rates
of dispersal and little gene flow among populations, particularly those
that are separated by large geographic distances and deep ocean
expanses. Genetic variability within the species has likely been
reduced due to bottleneck events and genetic drift in the small and
isolated N. pompilius populations throughout its range. Additionally,
the data indicate that the chambered nautilus is a slow-growing and
late-maturing species (with maturity estimated between 10 and 17 years,
and longevity at least 20 years) with likely very low productivity and,
thus, is extremely susceptible to decreases in its abundance. In fact,
the data suggest that many chambered nautilus populations are in
decline and may be extirpated in the next several decades.
The comments that we received on the proposed rule provided
information that was either already considered in our analysis, was not
substantial or relevant, or was consistent with or reinforced
information in the status review report and proposed rule. Therefore,
our consideration of the information received has not altered our
analysis of the demographic risks to the species.
Summary of ESA Section 4(a)(1) Factors Affecting the Chambered Nautilus
As stated previously and as discussed in the proposed rule (82 FR
48948, October 23, 2017), we considered whether any one or a
combination of the five threat factors specified in section 4(a)(1) of
the ESA are contributing to the extinction risk of the chambered
nautilus and result in the species meeting the definition of
``endangered species'' or ``threatened species.'' The primary threat to
the chambered nautilus is overutilization through commercial harvest to
meet the demand for the international nautilus shell trade. Out of the
10 nations where N. pompilius is known to occur, potentially half have
targeted nautilus fisheries either historically or currently. These
waters comprise roughly three-quarters of the species' known range.
Current estimated levels of harvest to meet the international demand
are projected to lead to extirpations of local N. pompilius populations
as has been observed in the past. Additionally, efforts to address
overutilization of the species through regulatory measures appear
inadequate, with evidence of targeted fishing of and trade in the
species, particularly in Indonesia, Philippines, and China, despite
prohibitions.
The comments that we received on the proposed rule provided
information that was either already considered in our analysis, was not
substantial or relevant, or was consistent with or reinforced
information in the status review report and proposed rule. Therefore,
our consideration of the information received has not led us to change
our conclusions regarding any of the section 4(a)(1) factors or their
interactions. All of the information, discussion, and conclusions
regarding the factors affecting the chambered nautilus contained in the
final status review report (Miller 2018) and the proposed rule is
reaffirmed in this final action.
[[Page 48982]]
Extinction Risk
As discussed previously, the status review report evaluated the
demographic risks to the chambered nautilus according to four
categories--abundance and trends, population growth/productivity,
spatial structure/connectivity, and genetic diversity. As a concluding
step, after considering all of the available information regarding
demographic and other threats to the species, we rated the species'
extinction risk according to a qualitative scale (high, moderate, and
low risk). We found that N. pompilius is at a moderate risk of
extinction throughout its range. We explained in the proposed rule that
a species is at a ``moderate risk'' of extinction when it is on a
trajectory that puts it at a high level of extinction risk in the
foreseeable future. A species may be at moderate risk of extinction
because of projected threats or declining trends in abundance,
productivity, spatial structure, or diversity. While the chambered
nautilus is still traded in considerable amounts (upwards of thousands
to hundreds of thousands annually), with evidence of new sites being
established for nautilus fishing (e.g., in Indonesia, Philippines,
Papua New Guinea), and areas of stable, unfished populations (e.g.,
eastern Australia, American Samoa), we concluded that without adequate
measures controlling the overutilization of the species, N. pompilius
is on a trajectory where its overall abundance will likely see
significant declines within the foreseeable future eventually reaching
the point where the species' continued persistence will be in jeopardy.
We, therefore, determined that the species is not presently in danger
of extinction throughout its range but is likely to become so within
the foreseeable future (i.e., the species is a threatened species).
Because we find that the chambered nautilus is likely to become an
endangered species within the foreseeable future throughout its range,
we do not go on to consider whether the species might be threatened or
endangered in a significant portion of its range, for the reasons
explained in the Listing Species Under the Endangered Species Act
section above and more fully in the proposed rule.
The information received from public comments on the proposed rule
was either already considered in our analysis, was not substantial or
relevant, or was consistent with or reinforced information in the
status review report and proposed rule. Therefore, our consideration of
the information received has not altered our view of the extinction
risk of the chambered nautilus. Our conclusion regarding the extinction
risk for the chambered nautilus remains the same. Therefore, all of the
information, discussion, and conclusions on the extinction risk of the
chambered nautilus contained in the final status review report and the
proposed rule is reaffirmed in this final action.
Protective Efforts
In addition to regulatory mechanisms (considered under ESA section
4(a)(1)(D)), we considered other efforts being made to protect the
chambered nautilus (pursuant to ESA section 4(b)(1)(A)). The efforts we
evaluated included a non-profit campaign devoted to raising the
awareness of threats to the chambered nautilus and the potential for
aquaculture or artificial propagation programs to satisfy the trade
industry demand for shells and restore wild populations. We considered
whether such protective efforts sufficiently ameliorated the identified
threats to the point that they would alter the conclusions of the
extinction risk analysis for the species so as to possibly avoid the
need to list. None of the information we received on the proposed rule
affected our conclusions regarding conservation efforts to protect the
chambered nautilus. Thus, all of the information, discussion, and
conclusions on the protective efforts for the chambered nautilus
contained in the final status review report and proposed rule are
reaffirmed in this final action.
Final Determination
We have reviewed the best available scientific and commercial
information, including the petition, the information in the final
status review report (Miller 2018), the comments of peer reviewers, and
public comments. None of the information received since publication of
the proposed rule (82 FR 48948, October 23, 2017) altered our analyses
or conclusions that led to our determination for the chambered
nautilus. Therefore, the determination in the proposed rule is
reaffirmed in this final rule and stated below.
Based on the best available scientific and commercial information,
and after considering efforts being made to protect N. pompilius, we
conclude that the chambered nautilus is not currently in danger of
extinction throughout its range but is likely to become so in the
foreseeable future throughout all of its range from threats of
overutilization and the inadequacy of existing regulatory mechanisms.
Therefore, we have determined that the chambered nautilus meets the
definition of a ``threatened species'' and list it is as such
throughout its range under the ESA.
Effects of Listing
Conservation measures provided for species listed as endangered or
threatened under the ESA include designation of critical habitat, to
the maximum extent prudent and determinable (16 U.S.C. 1533(a)(3)(A));
development of recovery plans (16 U.S.C. 1533(f)); Federal agency
consultations with NMFS under section 7 of the ESA to ensure their
actions are not likely to jeopardize the species or result in adverse
modification or destruction of critical habitat, should it be
designated (16 U.S.C. 1536); and, for endangered species, prohibitions
on taking and certain other activities (16 U.S.C. 1538). Prohibitions
on taking, or other protections, may also be extended through
regulation to threatened species. (16 U.S.C. 1533(d)). In addition,
recognition of the species' imperiled status through listing can
indirectly inform voluntary conservation actions by Federal and State
agencies, foreign entities, private groups, and individuals.
Protective Measures and Prohibitions
Section 7(a)(2) (16 U.S.C. 1536(a)(2)) of the ESA and NMFS/USFWS
regulations (50 CFR part 402) require Federal agencies to consult with
us to ensure that activities they authorize, fund, or carry out are not
likely to jeopardize the continued existence of listed species or
destroy or adversely modify critical habitat. Our section 7 regulations
require the responsible Federal agency to initiate formal consultation
if a Federal action may affect a listed species or its critical habitat
(50 CFR 402.14(a)). Examples of Federal actions that may affect the
chambered nautilus include: Fishery harvest and management practices,
energy projects, discharge of pollution from point sources, non-point
source pollution, dredging, mining, pile-driving, military activities,
toxic waste and other pollutant disposal, and shoreline development.
This list is not exhaustive, and the extent to which consultation is
required will depend on the particular facts of any particular proposed
Federal action.
In the case of threatened species, ESA section 4(d) gives the
Secretary discretion to issue such regulations as he or she deems
necessary and advisable for the conservation of the species. 16 U.S.C.
1533(d). The Secretary may also decide to extend some or all the
prohibitions of section 9(a)(1) of the ESA (16 U.S.C. 1538(a)(1)) to
the species.
[[Page 48983]]
As mentioned in the status review report and proposed rule, all
nautilus species were included on Appendix II of CITES in October 2016,
with the listing going into effect in January 2017. Export of nautilus
products, such as shells, requires CITES permits that ensure the
products were legally acquired and that the Scientific Authority of the
State of export has advised that such export will not be detrimental to
the survival of that species (after taking into account factors such as
its population status and trends, distribution, harvest, and other
biological and ecological elements). In the proposed rule, this CITES
protection was determined not to have ameliorated the threats to the
threatened chambered nautilus because the CITES listing had only
recently gone into effect and, therefore, we lacked information that
would allow us to fully evaluate its adequacy in decreasing the threat
of overutilization. We are still in the process of collecting
information in order to evaluate the effectiveness of this CITES
Appendix II listing of the chambered nautilus as a tool to ensure the
sustainable trade in this species. If we determine that additional
measures may be necessary to safeguard the species against future
depletion of populations or potential extinction of the chambered
nautilus, then we may issue protective regulations under section 4(d)
or extend some or all of the prohibitions of section 9(a)(1) of the ESA
that automatically apply with respect to endangered species. However,
at this time, we are not proposing to apply such prohibitions to the
chambered nautilus. We may consider potential protective regulations
pursuant to section 4(d) for chambered nautilus in a future rulemaking.
Critical Habitat
Critical habitat is defined in section 3 of the ESA (16 U.S.C.
1532(5)) as: (1) The specific areas within the geographical area
occupied by a species, at the time it is listed, on which are found
those physical or biological features (a) essential to the conservation
of the species and (b) that may require special management
considerations or protection; and (2) specific areas outside the
geographical area occupied by a species at the time it is listed upon a
determination that such areas are essential for the conservation of the
species. ``Conservation'' means the use of all methods and procedures
needed to bring the species to the point at which listing under the ESA
is no longer necessary (i.e., the point at which it is ``recovered'').
16 U.S.C. 1532(3). Section 4(a)(3)(A) of the ESA (16 U.S.C.
1533(a)(3)(A)) requires that, to the maximum extent prudent and
determinable, critical habitat be designated concurrently with the
listing of a species. Designations of critical habitat must be based on
the best scientific data available and must take into consideration the
economic, national security, and other relevant impacts of specifying
any particular area as critical habitat.
At this time, we find that critical habitat for the chambered
nautilus is not determinable because data sufficient to perform the
required analyses are lacking. As stated in the status review report
and proposed rule, while it is known that chambered nautiluses are
extreme habitat specialists, found in association with steep-sloped
forereefs with sandy, silty, or muddy-bottomed substrates, and in
depths from around 100 meters to 500 meters, the presence of these
features does not necessarily indicate the likelihood of chambered
nautilus occurrence. Chambered nautiluses have a patchy distribution
and, given the difficulty associated with accessing their habitat and
observing the species for research purposes, very little is known
regarding important aspects of the species' life history, such as
reproduction and growth in the wild. As such, we find that sufficient
information is not currently available to: (1) Identify the physical
and biological features essential to conservation of the species at an
appropriate level of specificity, particularly given the uncertainty
regarding habitat features necessary to support important life history
needs and the irregularity and unpredictability of chambered nautiluses
within areas they are known to occur, (2) determine the specific
geographical areas that contain the physical and biological features
essential to conservation of the species, and (3) assess the impacts of
the designation. Therefore, public input on features and areas under
U.S. jurisdiction that may meet the definition of critical habitat for
the chambered nautilus is invited. Additional details about specific
types of information sought are provided in the Information Solicited
section later in this document. Input may be sent to the Office of
Protected Resources in Silver Spring, Maryland (see ADDRESSES). Please
note that we are not required to respond to any input provided on this
matter.
Information Solicited
Because critical habitat is not currently determinable for the
chambered nautilus, we are not proposing to designate critical habitat
in this rulemaking. We request interested persons to submit relevant
information regarding the identification of critical habitat of the
chambered nautilus, including specific areas within the geographical
area occupied by the species that include the physical or biological
features essential to the conservation of the species and that may
require special management considerations or protection. Areas outside
the occupied geographical area should also be identified if such areas
themselves are essential for the conservation of the species. ESA
implementing regulations at 50 CFR 424.12(g) specify that critical
habitat shall not be designated within foreign countries or in other
areas outside of U.S. jurisdiction. Therefore, we request information
only on potential areas of critical habitat within U.S. jurisdiction.
Section 4(b)(2) of the ESA requires the Secretary to consider the
economic impact, impact on national security, and any other relevant
impact of designating a particular area as critical habitat. Section
4(b)(2) also gives the Secretary discretion to consider excluding from
a critical habitat designation any particular area where the Secretary
finds that the benefits of exclusion outweigh the benefits of including
the area in the designation, unless excluding that area will result in
extinction of the species.
To inform our consideration of potential critical habitat, we also
request information describing the following with respect to the
relevant features or areas: (1) Activities that may affect the
essential features or threats to the essential features, or to an area
of potential critical habitat itself; (2) activities that could be
affected by designating specific areas as critical habitat; and (3) the
positive and negative economic, national security and other relevant
impacts, including benefits to the recovery of the species, likely to
result if specific areas are designated as critical habitat. We seek
information regarding the conservation benefits of designating areas
under U.S. jurisdiction as critical habitat. In keeping with the
guidance provided by the Office of Management and Budget (2000; 2003),
we seek information that would allow the monetization of these effects
to the extent possible, as well as information on qualitative impacts.
Information submitted may include, but need not be limited to: (1)
Scientific or commercial publications; (2) administrative reports, maps
or other graphic materials; and (3) information received from experts.
Information and data are particularly sought concerning: (1) Maps and
specific information describing the amount, distribution, and use type
(e.g., foraging, reproduction) of chambered nautilus habitats, as well
as any additional information on occupied
[[Page 48984]]
and unoccupied habitat areas; (2) the reasons why any habitat should or
should not be included in a designation of critical habitat under
sections 3(5)(A) and 4(b)(2) of the ESA; (3) information regarding the
benefits of designating particular areas as critical habitat or of
excluding particular areas; (4) current or planned activities in the
areas that might be proposed for designation and their possible
impacts; (5) any foreseeable economic or other potential impacts
resulting from designation, and in particular, any impacts on small
entities; (6) whether specific unoccupied areas may be essential to
provide additional habitat areas for the conservation of the species;
and (7) potential peer reviewers for a proposed critical habitat
designation, including persons with biological and economic expertise
relevant to the species, region, and designation of critical habitat.
We solicit information from the public, other concerned governmental
agencies, the scientific community, industry, or any other interested
party (see ADDRESSES).
References
A list of all references cited in this final rule is available at
www.regulations.gov (identified by docket number NOAA-NMFS-2016-0098)
or available upon request (see ADDRESSES). The peer review report is
available at: https://www.cio.noaa.gov/services_programs/prplans/PRsummaries.html. Additional information can be found on our website at
https://www.fisheries.noaa.gov/species/chambered-nautilus.
Classification
National Environmental Policy Act
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), NMFS has concluded that ESA listing actions are not subject to
the environmental assessment requirements of the National Environmental
Policy Act (NEPA). (See NOAA Administrative Order 216-6A (2016) and
Companion Manual ``Policy and Procedures for Compliance with the
National Environmental Policy Act and Related Authorities'' at 2
(2017).
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 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 13771, Reducing Regulation and Controlling Regulatory
Costs
This rule is not an E.O. 13771 regulatory action because this rule
is exempt from review under E.O. 12866.
Executive Order 13132, Federalism
E.O. 13132 requires agencies to take into account any federalism
impacts of regulations under development. It includes specific
directives for consultation in situations where a regulation will
preempt state law or impose substantial direct ccompliance costs on
state and local governments (unless required by statute). Neither of
those circumstances is applicable to this final rule; therefore this
action does not have federalism implications as that term is defined in
E.O. 13132. 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.
List of Subjects in 50 CFR Part 223
Endangered and threatened species.
Dated: September 24, 2018.
Samuel D. Rauch, III,
Deputy Assistant Administrator for Regulatory Programs, National Marine
Fisheries Service.
For the reasons set out in the preamble, 50 CFR part 223 is amended
as follows:
PART 223--THREATENED MARINE AND ANADROMOUS SPECIES
0
1. The authority citation for part 223 continues to read as follows:
Authority: 16 U.S.C. 1531-1543; subpart B, Sec. 223.201-202
also issued under 16 U.S.C. 1361 et seq.; 16 U.S.C. 5503(d) for
Sec. 223.206(d)(9).
0
2. In Sec. 223.102, amend the table in paragraph (e) by adding a
subheading for ``Molluscs'' after the entry for ``Sturgeon, green''
under the ``Fishes'' subheading, and by adding an entry for ``Nautilus,
chambered'' underneath the ``Molluscs'' table subheading to read as
follows:
Sec. 223.102 Enumeration of threatened marine and anadromous species.
* * * * *
(e) * * *
--------------------------------------------------------------------------------------------------------------------------------------------------------
Species \1\ Citation(s) for
----------------------------------------------------------------------------------------------- listing Critical ESA rules
Common name Scientific name Description of listed entity determination(s) habitat
--------------------------------------------------------------------------------------------------------------------------------------------------------
* * * * * * *
--------------------------------------------------------------------------------------------------------------------------------------------------------
Molluscs
--------------------------------------------------------------------------------------------------------------------------------------------------------
Nautilus, chambered................ Nautilus pompilius.... Entire species................... [Insert Federal NA NA
Register page where
the document begins],
September 28, 2018.
* * * * * * *
--------------------------------------------------------------------------------------------------------------------------------------------------------
\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. 2018-21114 Filed 9-27-18; 8:45 am]
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