Endangered and Threatened Wildlife and Plants; 12-Month Finding on a Petition to List Agave eggersiana, 57720-57734 [2010-23571]
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Federal Register / Vol. 75, No. 183 / Wednesday, September 22, 2010 / Proposed Rules
and since the numbers of contractors
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or pricing data are a minute subset of
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List of Subjects in 48 CFR Part 52
Dated: September 15, 2010.
Edward Loeb,
Director, Acquisition Policy Division.
PART 52—SOLICITATION PROVISIONS
AND CONTRACT CLAUSES
1. The authority citation for 48 CFR
part 52 continues to read as follows:
Authority: 40 U.S.C. 121(c); 10 U.S.C.
chapter 137; and 42 U.S.C. 2473(c).
2. Amend section 52.214–27 by—
a. Revising the date of the clause; and
b. Removing from paragraph (e)(1)
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compounded daily, as required by 26
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The revised text reads as follows:
52.214–27 Price Reduction for Defective
Cost or Pricing Data—Modifications—
Sealed Bidding.
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3. Amend section 52.215–10 by—
a. Revising the date of the clause; and
b. Removing from paragraph (d)(1)
‘‘Simple interest’’ and adding ‘‘Interest
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52.215–10 Price Reduction for Defective
Cost or Pricing Data.
DATES:
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Price Reduction for Defective Cost or
Pricing Data (Date)
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4. Amend section 52.215–11 by—
a. Revising the date of the clause; and
b. Removing from paragraph (e)(1)
‘‘Simple interest’’ and adding ‘‘Interest
compounded daily, as required by 26
U.S.C. 6622,’’ in its place.
The revised text reads as follows:
52.215—11 Price Reduction for Defective
Cost or Pricing Data—Modifications.
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Price Reduction for Defective Cost or
Pricing Data-Modifications (Date)
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[FR Doc. 2010–23589 Filed 9–21–10; 8:45 am]
BILLING CODE 6820–EP–P
DEPARTMENT OF THE INTERIOR
50 CFR Part 17
Therefore, DoD, GSA, and NASA
propose amending 48 CFR part 52 as set
forth below:
*
period the status of the candidate taxon
will be addressed through our annual
Candidate Notice of Review (CNOR).
Fish and Wildlife Service
Government procurement.
*
compounded daily, as required by 26
U.S.C. 6622,’’ in its place.
The revised text reads as follows:
[Docket number FWS-R4-ES-2010-0051]
[MO 92210-0-0008-B2]
Endangered and Threatened Wildlife
and Plants; 12-Month Finding on a
Petition to List Agave eggersiana (no
common name) as Endangered
Fish and Wildlife Service,
Interior.
ACTION: Notice of 12–month petition
finding.
AGENCY:
We, the Fish and Wildlife
Service (Service), announce a 12–month
finding on a petition to list the plant
Agave eggersiana (no common name) as
endangered under the Endangered
Species Act of 1973, as amended (Act).
After review of all available scientific
and commercial information, we find
that listing A. eggersiana is warranted.
Currently, however, listing A.
eggersiana is precluded by higher
priority actions to amend the Lists of
Endangered and Threatened Wildlife
and Plants. Upon publication of this 12month petition finding, we will add A.
eggersiana to our candidate species list.
We will develop a proposed rule to list
A. eggersiana as our priorities allow. We
will make any determination on critical
habitat during development of the
proposed listing rule. In any interim
SUMMARY:
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The finding announced in this
document was made on September 22,
2010.
This finding is available on
the Internet at https://
www.regulations.gov at Docket Number
[FWS-R4-ES-2010-0051]. Supporting
documentation we used in preparing
this finding is available for public
inspection, by appointment, during
normal business hours at the U.S. Fish
and Wildlife Service, Caribbean
Ecological Services Field Office, Road
301, Km. 5.1, Boquero´n, Puerto Rico
00622. Please submit any new
information, materials, comments, or
questions concerning this species or this
finding to the above internet address or
the mailing address listed under FOR
FURTHER INFORMATION CONTACT.
ADDRESSES:
Ms.
Marelisa Rivera, Assistant Field
Supervisor, Caribbean Ecological
Services Field Office, P.O. Box 491,
Boquero´n, Puerto Rico 00622; by
telephone at (787) 851-7297; or by
facsimile at (787) 851-7440. Persons
who use a telecommunications device
for the deaf (TDD) may call the Federal
Information Relay Service (FIRS) at 800877-8339.
FOR FURTHER INFORMATION CONTACT:
Background
Section 4(b)(3)(A) of the Act (16
U.S.C. 1531 et seq.) requires that, for
any petition to revise the Federal Lists
of Threatened and Endangered Wildlife
and Plants that contains substantial
scientific or commercial information
that listing a species may be warranted,
we make a finding within 12 months of
the date of receipt of the petition. In this
finding, we determine whether the
petitioned action is: (a) Not warranted,
(b) warranted, or (c) warranted, but
immediate proposal of a regulation
implementing the petitioned action is
precluded by other pending proposals to
determine whether species are
threatened or endangered, and
expeditious progress is being made to
add or remove qualified species from
the Federal Lists of Endangered and
Threatened Wildlife and Plants. Section
4(b)(3)(C) of the Act requires that we
treat a petition for which the requested
action is found to be warranted but
precluded as though resubmitted on the
date of such finding, that is, requiring a
subsequent finding to be made within
12 months. We must publish these 12–
month findings in the Federal Register.
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Previous Federal Actions
Species Information
We identified Agave eggersiana as a
category 2 candidate species in the
Notice of Review published in the
Federal Register on September 30, 1993
(58 FR 51144) and subsequent
publication. A category 2 species was
one for which the Service had
information that proposing as
endangered or threatened may be
appropriate but for which sufficient
information was not currently available
to support a proposed rule. Designation
of category 2 species was discontinued
in the February 28, 1996, Notice of
Review (61 FR 7596). This notice
redefined candidates to include only
species for which we have information
needed to propose them for listing, and
as a result, Agave eggersiana was
removed from the Candidate species
list.
On November 21, 1996, we received
a petition from the U.S. Virgin Islands
Department of Planning and Natural
Resources (DPNR) requesting that we
list Agave eggersiana and Solanum
conocarpum as endangered. On
November 16, 1998, we published in the
Federal Register (63 FR 63659) our
finding that the petition to list A.
eggersiana and S. conocarpum
presented substantial information
indicating that the requested action may
be warranted and initiated a status
review on these two plants. On
September 1, 2004, the Center for
Biological Diversity filed a lawsuit
against the Department of the Interior
and the U.S. Fish and Wildlife Service
(Service) alleging that the Service failed
to publish a 12–month finding for A.
eggersiana and S. conocarpum (Center
for Biological Diversity v. Norton, Civil
Action No. 1:04-CV-2553 CAP). In a
stipulated settlement agreement
resolving that case, signed April 27,
2005, we agreed to submit our 12–
month finding for A. eggersiana and S.
conocarpum to the Federal Register by
February 28, 2006. On March 7, 2006,
we published our 12–month finding (71
FR 11367) that listing of A. eggersiana
and S. conocarpum was not warranted.
On September 9, 2008, the Center for
Biological Diversity filed a complaint
challenging our 12–month finding
(Center for Biological Diversity v.
Hamilton, Case No. 1:08-cv-02830
-CAP). In a settlement agreement
approved by the Court on August 21,
2009, the Service agreed to submit to the
Federal Register a new 12–month
finding for A. eggersiana by September
17, 2010. This notice constitutes the 12–
month finding on the 1996 petition to
list A. eggersiana as endangered.
Taxonomy and Species Description
Agave eggersiana is a flowering plant
of the family Agavaceae (century plant
family) endemic to the island of St.
Croix in the U.S. Virgin Islands. A.
eggersiana was originally described in
1913 by Trelease from material collected
on St. Croix, and is distinguished from
other members of the Agavaceae family
by its acaulescent (without an evident
leafy stem), non-suckering growth habit
(vegetative reproduction that does not
form offshoots around its base), and
fleshy, nearly straight leaves with small
marginal prickles (1.00 millimeter (mm);
0.04 inches (in) long) that are nearly
straight (Britton and Wilson 1923, p.
156; Proctor and Acevedo-Rodri´guez
2005, p. 118). Its flowers are deep
yellow, 5 to 6 centimeters (cm) (1.95 to
2.34 in) long. After flowering, the
panicles (inflorescence) produce
numerous small vegetative bulbs
(bulbils), from which the species can be
propagated (Proctor and AcevedoRodri´guez 2005, p. 118). Avave
eggersiana is not known to produce
fruit. Furthermore, based on
observations of cultivated plants, Agave
eggersiana requires at least 10 to 15
years to develop as a mature individual
and to produce an inflorescence (David
Hamada, St. George Botanical Garden,
2010, pers. comm.). Avave eggersiana
like other Agave species are
monocarpic, meaning the plant dies
after producing the spike or
inflorescence.
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Habitat and Distribution
Britton and Wilson (1923, p. 156)
reported the species from hillsides and
plains in the eastern dry districts of St.
Croix but did not provide population
estimates. In addition, Agave eggersiana
is cultivated on St. Croix and St.
Thomas for ornament (Trelease 1913, p.
28; Britton and Wilson 1923, p. 156;
Proctor and Acevedo-Rodri´guez 2005,
p. 118). Information provided in the
petition (Kojis and Boulon, DPNR, 1996,
pers. comm.) specified that the species
was last observed growing in the wild
around 1984 to 1986 on St. Croix. In
2003, DPNR stated that the species is
believed to be extinct (Plaskett 2003,
pers. comm.; Dalmida-Smith 2010, pers.
comm.). Proctor and AcevedoRodri´guez (2005, p. 118) provided a
general description of the species and
they state that the species ‘‘now appears
to be extinct in the wild.’’ However, no
citations or survey information were
provided to support this statement.
Subsequently, in 2010, DPNR provided
information based on field visits and
reported the existence of several
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populations in St. Croix (Dalmida-Smith
2010, pers. comm.).
Current Status
Historically, Agave eggersiana was
reported from the north coast in
Christiansted, St. Croix and along the
south coast of the island. The current
distribution and rarity of the species do
not represent the historical range.
Historically, sugar cane was the main
crop on the island and dominated the
economy for nearly 200 years (Shaw,
1933, p. 414). Apparently, the former
land use of the areas used for sugar cane
cultivation resulted in degradation of
the species’ habitat and nearly
extirpated the species from the wild.
Sugarcane is no longer cultivated on the
island and the majority of the areas
formerly used for sugarcane plantations
are currently grasslands and early
secondary forests dominated by the
exotic tree Leucaena leucocephala
(tantan).
In 2010, the Division of Fish and
Wildlife of the DPNR (Dalmida-Smith
2010, pers. comm.) conducted a local
status review to determine the extent of
the populations of Agave eggersiana in
St. Croix. They reported five sites where
the species was found; however, it is
uncertain if these populations are
natural populations (individuals that
come from wild populations) or if the
populations consist of individuals that
escaped from landscaping. The five
reported sites are: (1) Manchineel/
Ha’penny Beach (Southern St. Croix)
with an estimated 30 individuals, which
is approximately half the number of
individuals that they encountered 2
years before; (2) West side of Vagthus
point (Southern St. Croix ) with a single
individual; (3) Gallows Bay (Northern
St. Croix) with several plants but no
approximate number was mentioned; (4)
Protestant Cay (Northern St. Croix) with
an estimated 30 individuals, including a
number of young plants; and (5) Ruth
Island (Southern St. Croix) with a single
individual that was introduced to the
cay many years ago. However, the exact
year of this introduction is unknown.
In February 2010, Service biologists
conducted surveys of Agave eggersiana
on St. Croix. In their 2010 surveys,
Service biologists visited seven of the
ten currently known populations (Table
1). They did not survey the two areas
where a single individual has been
reported (Ruth Island and West Vagthus
point) or Buck Island Reef National
Monument, where individuals have
been planted and recent survey
information exists. Based on their
characteristics (growing mixed with
native vegetation, evidence of natural
recruitment and the presence of
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different size classes), these surveys
indicate that the species currently
occurs in six areas that appear to be
remnants of wild populations. Four
localities (Buck Island Reef National
Monument, Salt River Bay, Ruth Island,
and Lagoon Picnic Area) contain
individuals that were planted in recent
years.
TABLE 1. CURRENTLY KNOWN POPULATIONS OF Agave eggersiana ON ST. CROIX.
Category
Estimated # of Adult
Individuals
Source of Information
Manchineel / Ha’penny Beach
Wild
25–30
Dalmida-Smith 2010, pers. comm.; Monsegur and Vargas
2010, unpublished data
West Vagthus point
Wild
1
Gallows Bay
Wild
2–3
David Hamada. 2010, pers. comm.; Monsegur and Vargas
2010, unpublished data.
Protestant Cay
Wild
30–51 + 60 bulbils
Dalmida-Smith 2010, pers. comm.; Monsegur and Vargas
2010, unpublished data
Ruth Island
Introduced*
1
Great Pond
Wild
76 + 50 bulbils
South Shore
Wild
100 + 150 bulbils
Monsegur and Vargas 2010, unpublished data.
Salt River Bay
Introduced**
6
Monsegur and Vargas 2010, unpublished data.
Buck Island National Monument
Introduced*
5
Monsegur and Vargas 2010, unpublished data.
Lagoon Picnic Area
Landscape
177
Monsegur and Vargas 2010, unpublished data.
Locality
Total
Dalmida-Smith 2010. pers. comm.
Dalmida-Smith 2010, pers. comm.
Monsegur and Vargas 2010, unpublished data; Plaskett 2003.
pers. comm.
450 +260 bulbils
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* Introduced by DPNR for conservation.
** Introduced by NPS for education and outreach.
The eight localities containing
multiple Agave eggersiana plants are
described as follows:
(1) Gallows Bay (private property) has
several individuals that are considered
by local experts as a remnant of a
natural population (David Hamada
2010, pers. comm.). Historical
documents and illustrations show that
Agave eggersiana was common on the
landscape of Gallows Bay (David
Hamada 2010, pers. comm.).
(2) Protestant Cay (owned by the
government but leased to a private
party), has an estimated population of
51 adult individuals of different sizes
and about 60 bulbils.
(3) Ha’penny Beach (private property),
has an estimated population of 25
individuals of different size classes; one
of the plants was found flowering
during the site visit conducted by the
Service in 2010.
(4) Great Pond (managed by the
Department of Housing, Parks and
Recreation) has a healthy population of
A. eggersiana with different size plants
and evidence of recent flowering events.
This population is located near Great
Pond, an area where it was suspected
that descendants from wild plants may
have existed (Plaskett 2003, pers.
comm.).
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(5) South Shore (private property), has
a population of about 100 adult
individuals and about 150 bulbils, all
growing on small terraces at a rocky
cliff. This population is actively
flowering and it was noted that some of
the bulbils are reaching the sea,
suggesting a possible dispersal
mechanism for the species.
(6) Salt River Bay National Historic
Park and Ecological Preserve (SARI)
(managed by the National Park Service
(NPS)) has six individual plants. In
2007, personnel from the NPS planted
these individuals at Salt River as part of
the landscape with the idea of
establishing a population at the site and
for outreach purposes. At the time of the
survey, five of these plants were
producing spikes and were expected to
produce bulbils within the following
months (Monsegur and Vargas, USFWS,
2010, unpublished data). Based on
information provided by personnel from
NPS, additional propagation efforts with
the species are planned in the near
future (Lundgreen 2010, pers. comm.).
(7) Buck Island Reef National
Monument (managed by the NPS) has
an estimated population of five
individuals. In 2007, personnel from
NPS planted these five individuals on
the island, but at present time there is
no information regarding the breeding
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condition of these plants (Lundgreen
2010, pers. comm.).
(8) Lagoon Picnic Area (a public
beach area that seems to be under a
reforestation effort funded by the
Antilitter and Beautification
Commission) harbors about 177 plants
as part of the landscape. The size of the
individuals in this area ranges from
small planted bulbils to a few adult
individuals ready to flower. Based on
the information gathered and
observations, about 450 adult
individuals and 260 bulbils are
currently known in 10 localities,
including 6 populations that are
considered wild, 3 introduced
populations for conservation and public
education, and 1 landscape population
(Table 1). In addition to these localities,
Monsegur and Vargas (2010, personal
observation) documented the species
presence in private gardens scattered
throughout the island. We estimate
about 90 adult individuals are present
in these private gardens.
At the present time, information on
ecology, phenology, and genetics for
Agave eggersiana is lacking. Samples of
A. eggersiana from individuals in the
Gallows Bay area have been collected
for genetics analysis, but results were
not available prior to making this
finding (Ray 2010, pers. comm.).
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Current evidence suggests that the wild
and cultivated populations have
minimum genetic variation. Therefore,
all A. eggersiana plants (cultivated and
wild) are included as part of the listable
entity in this finding; however, we have
focused our assessment of threats to the
wild populations. Although data suggest
that cultivated individuals could be
used as genetic stock to aid in the longterm survival of this species, most
cultivated populations are groomed to
prevent recruitment and thus offer
minimal conservation contribution. We
do not feel that cultivated individuals
propagated for private or commercial
uses aid in the conservation or the
recovery of the species in the wild.
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Summary of Information Pertaining to
the Five Factors
Section 4 of the Act (16 U.S.C. 1533),
and implementing regulations (50 CFR
424), set forth procedures for adding
species to the Federal Lists of
Endangered and Threatened Wildlife
and Plants. Under section 4(a)(1) of the
Act, a species may be determined to be
endangered or threatened based on any
of the following five factors: (A) The
present or threatened destruction,
modification, or curtailment of its
habitat or range; (B) overutilization for
commercial, recreational, scientific, or
educational purposes; (C) disease or
predation; (D) the inadequacy of
existing regulatory mechanisms; or (E)
other natural or manmade factors
affecting its continued existence. In
making this finding, information
pertaining to Agave eggersiana, in
relation to the five factors provided in
section 4(a)(1) of the Act is discussed
below.
In considering what factors might
constitute threats to a species, we must
look beyond the exposure of the species
to a factor to evaluate whether the
species may respond to the factor in a
way that causes actual impacts to the
species. If there is exposure to a factor
and the species responds negatively, the
factor may be a threat and we attempt
to determine how significant a threat it
is. The threat is significant if it drives,
or contributes to, the risk of extinction
of the species such that the species
warrants listing as endangered or
threatened as those terms are defined in
the Act.
Factor A: The Present or Threatened
Destruction, Modification, or
Curtailment of the Species’ Habitat or
Range
Of the currently known populations,
only three areas are managed for
conservation (Ruth Island, Salt River
Bay, and Buck Island National
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Monument), the remaining populations
occur within privately owned lands
currently threatened by development or
areas already developed and managed as
tourism and residential projects. Based
on information reported by the
University of the Virgin Islands’
Conservation Data Center (https://
cdc.uvi.edu), at least three of the
populations (Protestant Cay, Gallows
Bay, and Ha’penny Beach) lie within
areas identified by the DPNR as highdensity land use areas, which have a
higher susceptibility to development in
the near future. Furthermore, Weiss
(2010, pers. comm.) identified two
proposed development projects within
suitable habitat for the species (C&R
Robin, LLC and Seven Hills Beach
Resort and Casino). Based on the field
assessment conducted by Service
biologists, the coastal areas that harbor
suitable habitat for the species are
currently subject to urban and tourist
development (Monsegur and Vargas
2010, personal observation).
The population at Protestant Cay
seems to be affected by the use of the
area as a deposit for garden debris from
a hotel that occupies the majority of this
small island (Monsegur and Vargas
2010, personal observation). Since
Agave eggersiana relies on asexual
reproduction, the species depends on
the bulbils becoming established.
Covering the bulbils with debris may
result in subsequent mortality of the
bulbils and lack of natural recruitment,
thus affecting the long-term survival of
this population. Moreover, individuals
located on the edges of the population
are pruned as part of the gardens’
maintenance. This practice may result
in mortality or mutilation of individuals
since the species is monopodial (single
growth axis). The population at
Protestant Cay is also threatened by
competition with exotic plant species.
Individuals seem to be stressed due to
competition with exotics as what little
undeveloped habitat is left is rapidly
being colonized by nonnative species
(see Factor E).
The individuals located at Gallows
Bay are within an area currently
developed as a residential complex with
the potential for future expansion,
which may affect these individuals
(Monsegur and Vargas 2010, personal
observation). In addition, this area does
not contain additional habitat to allow
the current population to expand.
Remaining forested areas surrounding
this location are characterized by the
abundance of exotic species. Areas that
could be used by bulbils to become
established are occupied by the exotic
plant Sansevieria cilindrica, a species
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that tends to form a complete cover of
the understory (see Factor E).
The areas adjacent to Ha’penny Bay
on the south coast of St. Croix harbor
two of the known natural populations of
Agave eggersiana (Ha’penny Beach and
South Shore). According to personnel
from the DPNR (Valiulis 2010, pers.
comm.) these areas are advertised by
realtors as areas for tourism and
residential development and, as
previously mentioned, are planned for
high-density development. Furthermore,
the areas along the south coast that have
not been developed are used for cattle
or hay production, minimizing the
recovery of native vegetation and,
therefore, the habitat for A. eggersiana
(Monsegur and Vargas 2010, personal
observation). The development of
tourist and residential projects in these
coastal areas may result in the
extirpation of some populations, or at
the least, will reduce the chances of the
populations to expand or to colonize
other areas. This is exacerbated by the
low potential for natural recruitment
due to the small number of populations
and individuals.
The population of Great Pond is
located between the entrance road of the
East End Marine Park office and a
private property currently for sale. The
population seems to be healthy based on
the presence of different size plants and
evidence of recent flowering events. It
seems that there is suitable habitat for
the species in the area; however, the
area near the population is mowed and
the access road limits the expansion of
the population’s range. Furthermore, the
area adjacent to this population is a
private property for sale. The possible
use of the area for residential or tourist
development may affect the population;
owners will likely manage their
properties as landscapes, which could
lead to land clearing, additional
mowing, and other maintenance of
gardens. This could also lead to the
introduction of exotics. Moreover, the
abundance of grassland areas and the
dominance of the exotic Megathyrsus
maximus (guinea grass) in the area make
the population Agave eggersiana
susceptible to human-induced fires
(addressed in Factor E). These exotic
grasses are typically adapted to fire
conditions.
Based on the above information, we
consider the present or threatened
destruction, modification, or
curtailment of the species habitat or
range as a moderate but imminent threat
to wild populations of Agave
eggersiana. The threats of possible
construction developments and current
management of habitat of the
populations may further limit species
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propagation and expansion in the
foreseeable future.
Factor B: Overutilization for
Commercial, Recreational, Scientific, or
Educational Purposes
Agave eggersiana has been reported as
a cultivar since it was described as a
species in 1913 (Trelease, 1913, p. 28);
historically, the majority of A.
eggersiana found in St. Croix and St.
Thomas were from landscaped areas
(Britton and Wilson 1923, p. 156;
Plaskett 2003, pers. comm.; Kojis and
Boulon 1996, pers. comm.; Proctor and
Acevedo-Rodri´guez 2005, p. 118;
Acevedo-Rodri´guez 2005, pers. comm.).
The species is currently distributed by
the St. George Botanical Garden for
conservation and private landscaping
purposes. A. eggersiana is a commonly
used ornamental species on the island,
and recent declines in the number of
individuals at one population along the
coast of Ha’penny Bay are thought to be
due to collection for ornamental
purposes (Dalmida-Smith 2010, pers.
comm.; Valiulis 2010, pers. comm.).
Based on the above, we consider the
overutilization for commercial and
recreational purposes a moderate to low
but imminent threat to wild populations
of the species. Although captively
propagated Agave eggersiana are
available to residents for use in private
gardens, collection of wild individuals
is a threat to the species, and we expect
it to continue to be a threat in the
foreseeable future.
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Factor C: Disease or Predation
The genus Agave is widely affected by
the agave snout weevil (Scyphophorus
acupunctatus). This weevil has a wide
distribution that includes the Greater
Antilles (Cuba, Jamaica and Hispaniola)
(Vaurie 1971, p. 4). The larvae of this
weevil feed on the starchy base of the
plant, increasing the risk of infestation
by pathogens, such as a virus or fungus,
later resulting in the death of the plant
(Vaurie 1971, p. 4). At this time, there
is no information about the occurrence
of the agave snout weevil within the
Puerto Rican Platform or the Lesser
Antilles where St. Croix is located. A
small number of individuals of A.
eggersiana were observed with scarring
along the borders of some leaves
(Monsegur and Vargas 2010, personal
observation). It appears that an insect or
an arthropod larva may feed on the
leaves; however, the exact cause and the
consequences of the scarring are
unknown. Nevertheless, this is
important and it should be monitored as
it might be an indicator of a recently
arrived pest to St Croix.
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On Mona Island (Puerto Rico), feral
pigs are known to uproot juveniles and
destroy the root system of Agave
sisalana, to feed on the root system or
to use them as a water source (Saliva
1983, 1996, personal observation). Since
introduced pigs, donkeys, and goats
have been reported in St. Croix we
cannot discard the possible predation of
A. eggersiana by these feral animals,
particularly to young plants within the
populations. The absence of evidence of
predation by these species might be the
result of the low number of populations
of A. eggersiana, their isolation, and the
proximity of some of these populations
to human inhabited areas. However, at
this time, there is no evidence that
donkeys, pigs, or goats constitute a
specific threat to any A. eggersiana
populations.
Since the agave snout weevil has not
been reported in St. Croix, we do not
consider disease as a threat to the
species. Although there is some
evidence that insect or arthropod larvae
may feed on the leaves of Agave
eggersiana, there is no evidence that this
is negatively impacting the species’
ability to grow or reproduce. In
addition, we have no evidence of
grazing on A. eggersiana by introduced
donkeys, pigs, or goats. Therefore, we
do not find disease or predation to be
a current threat to the species.
Factor D: The Inadequacy of Existing
Regulatory Mechanisms
The Territory of the U.S. Virgin
Islands currently considers Agave
eggersiana to be endangered under the
Virgin Islands Indigenous and
Endangered Species Act (V.I. Code, Title
12, Chapter 2), and has amended an
existing regulation (Bill No. 18-0403) to
provide for protection of endangered
and threatened wildlife and plants by
prohibiting the take, injury, or
possession of indigenous plants. Based
on the number of individuals currently
used for private gardens and current
landscape practices in private areas,
such as pruning and mowing of
populations, we believe that protection
provisions under the local regulation are
not being appropriately enforced.
Rothenberger et al. (2008, p. 68)
mentioned that the lack of management
and enforcement capacity continues to
be a significant challenge for the USVI
since enforcement agencies are
chronically understaffed and territorial
resource management offices experience
significant staff turnover, particularly
during administration changes.
Based on the information above, we
consider the inadequacy of existing
regulatory mechanisms as a current
threat to the species due to a lack of
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enforcement. Because at least three
populations exist in areas managed for
conservation and public outreach, we
consider this threat to be moderate to
low in magnitude but imminent. We do
not anticipate any regulatory or
enforcement changes that would reduce
this threat in the foreseeable future.
Factor E: Other Natural or Manmade
Factors Affecting the Continued
Existence of the Species
The islands of the Caribbean are
frequently affected by hurricanes. It has
been suggested that hurricanes are
responsible for shaping and modifying
the structure and composition of the
vegetation in the Caribbean (Van Bloem
et al. 2003, p. 137; Van Bloem et al.
2005, p. 572; Van Bloem et al. 2006, p.
517). As an endemic species to the
island of St. Croix, Agave eggersiana
would be expected to be well adapted
to tropical storms. However, the low
number of individuals found on the
island and the reproductive biology of
the species (dependence on asexual
reproduction and the plant dying after
flowering) increases the likelihood of
stochastic events such as hurricanes
extirpating a population. We believe
that landslides and coastal erosion
associated with hurricanes may affect
the populations located along the
coastal areas of St. Croix (Ha’penny
Beach, South Shore, and Protestant Cay)
due to their proximity to cliffs and the
shoreline.
Agave eggersiana may be further
threatened by climate change, which is
predicted to increase the frequency and
strength of tropical storms and can
cause severe droughts (Hopkinson et al.
2008, p. 260). The cumulative effect of
coastal erosion due to severe hurricanes
plus the habitat modification for urban
and tourist development can further
diminish the availability of suitable
habitat and, therefore, limit population
expansion and colonization of new
areas. In addition, the possibility of
severe droughts may contribute to an
increase in the quantity and frequency
of fires on the island. These cumulative
factors may reduce the number of
individuals and further reduce
populations.
Based on satellite images, there is
evidence of human-induced fires along
the south coast of the island. The
vegetation of the Caribbean is not
adapted to fires since this disturbance
does not naturally occur on these
islands (Brandeis and Woodall 2008, p.
´
557; Santiago-Garcia et al. 2008, p. 608);
juvenile plants are especially vulnerable
to fire damage. This regime of humaninduced fires could modify the
landscape by promoting exotic trees and
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grasses, and by diminishing the seed
bank of native species. For example the
exotic Megathyrsus maximus is well
adapted to fires and typically colonizes
areas that were previously covered by
native vegetation. Furthermore, the
presence of this species increases the
amount of fuel and, therefore, the
intensity of the fire events. Due to the
abundance of grasses at Great Pond, this
Agave eggersiana population is
particularly threatened by humaninduced fires.
Moreover, the individuals of the
populations of Protestant Cay, Gallows
Bay and Great Pond are surrounded by
dense stands of different species of
Sansevieria, an herb native to Africa.
This invasive species seems to be
occupying the ecological niche adjacent
to the known populations of Agave
eggersiana. Plant invasion can affect the
environment at three levels; at the
genetic level the number of individuals
of native species can be reduced below
the minimum necessary for persistence,
at the species diversity level the number
of species present and their distribution
can be reduced, and at the ecosystem
level the functioning of the ecosystem
can be changed (Rippey et al. 2002, p.
170). In this case, invasive species may
constrain the number of A. eggersiana
reducing variability in the population.
Consequently, the loss of diversity of
the species may eliminate A. eggersiana
in the area affecting other organisms
(e.g., insects and birds feeding on the
flowers).
Based on the above information and
due to the reduced number of
populations and individuals, we believe
that the species is currently threatened
by natural or manmade factors such as
hurricanes, fires, and competition from
exotic species. Climate change may
exacerbate these habitat threats by
increasing the frequency of fires,
droughts, and hurricanes. We consider
these threats to be moderate and
imminent. We do not anticipate any
changes that would appreciably reduce
this threat in the foreseeable future.
Finding
As required by the Act, we conducted
a review of the status of the species and
considered the five factors in assessing
whether Agave eggersiana is threatened
or endangered throughout all or a
significant portion of its range. We
examined the best scientific and
commercial information available
regarding the past, present, and future
threats faced by the species. We
reviewed the petition, information
available in our files, other available
published and unpublished
information, consulted with species and
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habitat experts and other Federal and
State agencies, and conducted field
work on the island of St. Croix.
This status review identified threats
to the species attributable to Factors A,
B, D, and E. Of the currently known
populations, only three populations are
located in areas managed for
conservation and public outreach (Ruth
Island, Salt River Bay, and Buck Island
National Monument). The remaining
populations, containing about 97
percent of the currently known adult
individuals, are located in areas either
threatened by development pressure, or
are currently affected by landscape
practices and competition with exotic
species, resulting in detrimental effects
to reproduction and recruitment (see
Factors A and E). Furthermore, the use
of the Agave eggersiana as an
ornamental species is common on the
island, and evidence suggests that wild
specimens are being collected due to the
commercial interest in this species
(Factor B). Although the species is
currently listed under local regulations,
lack of enforcement of local law does
not provide adequate protection to
ameliorate threats to the species.
On the basis of the best scientific and
commercial information available and
our analysis of the current and
foreseeable threats to the species and its
habitat, we find that listing Agave
eggersiana (including wild and
cultivated populations), is warranted.
We will make a determination on the
status of the species as threatened or
endangered when we do a proposed
listing determination. However, as
explained in more detail below, an
immediate proposal of a regulation
implementing this action is precluded
by higher priority listing actions, and
progress is being made to add or remove
qualified species from the Lists of
Endangered and Threatened Wildlife
and Plants.
We reviewed the available
information to determine if the existing
and foreseeable threats render the
species at risk of extinction now such
that issuing an emergency regulation
temporarily listing the species as per
section 4(b)(7) of the Act is warranted.
We determined that issuing an
emergency regulation temporarily
listing the species is not warranted for
this species at this time since
approximately 450 individuals are
known to occur in 10 localities (Table
1). However, if at any time we
determine that issuing an emergency
regulation temporarily listing the
species is necessary, we will initiate this
action at that time.
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Listing Priority Number
The Service adopted guidelines on
September 21, 1983 (48 FR 43098), to
establish a rational system for utilizing
available resources for the highest
priority species when adding species to
the Lists of Endangered or Threatened
Wildlife and Plants or reclassifying
species listed as threatened to
endangered status. The system places
greatest importance on the immediacy
and magnitude of threats, but also
factors in the level of taxonomic
distinctiveness by assigning priority in
descending order to monotypic genera,
full species, and subspecies (or
equivalently, distinct population
segments of vertebrates).
We assigned Agave eggersiana an LPN
of 8, based on our finding that the
species faces moderate to low
magnitude threats from the present or
threatened destruction, modification, or
curtailment of its habitat; overutilization
for commercial, recreational, scientific,
or educational purposes; the inadequacy
of existing regulatory mechanisms; and
other natural or manmade Factors. One
or more of the threats discussed above
are occurring, and we anticipate they
will still occur in the near future in each
known population in St. Croix. These
threats are ongoing and in some cases
considered irreversible.
Although the species faces threats, as
described above, we believe these
threats to be of moderate to low
magnitude; at least 450 adults and 260
bulbils are known to occur in 10
populations with half showing evidence
of recruitment in the wild and 3 located
in areas managed for conservation and
public outreach. Under the 1983
Guidelines, a ‘‘species’’ facing imminent
moderate to low magnitude threats is
assigned an LPN of 7, 8, or 9 depending
on its taxonomic status. Because A.
eggersiana is a species, but not a
monotypic genus, we assigned it an LPN
of 8. While we conclude that listing the
species is warranted, an immediate
proposal to list this species is precluded
by other higher priority listing actions,
which we address below.
Preclusion and Expeditious Progress
Preclusion is a function of the listing
priority of a species in relation to the
resources that are available and
competing demands for those resources.
Thus, in any given fiscal year (FY),
multiple factors dictate whether it will
be possible to undertake work on a
proposed listing regulation or whether
promulgation of such a proposal is
warranted but precluded by higherpriority listing actions.
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Federal Register / Vol. 75, No. 183 / Wednesday, September 22, 2010 / Proposed Rules
The resources available for listing
actions are determined through the
annual Congressional appropriations
process. The appropriation for the
Listing Program is available to support
work involving the following listing
actions: proposed and final listing rules;
90–day and 12–month findings on
petitions to add species to the Lists of
Endangered and Threatened Wildlife
and Plants (Lists) or to change the status
of a species from threatened to
endangered; annual determinations on
prior ‘‘warranted but precluded’’ petition
findings as required under section
4(b)(3)(C)(i) of the Act; critical habitat
petition findings; proposed and final
rules designating critical habitat; and
litigation-related, administrative, and
program-management functions
(including preparing and allocating
budgets, responding to Congressional
and public inquiries, and conducting
public outreach regarding listing and
critical habitat). The work involved in
preparing various listing documents can
be extensive and may include, but is not
limited to: gathering and assessing the
best scientific and commercial data
available and conducting analyses used
as the basis for our decisions; writing
and publishing documents; and
obtaining, reviewing, and evaluating
public comments and peer review
comments on proposed rules and
incorporating relevant information into
final rules. The number of listing
actions that we can undertake in a given
year also is influenced by the
complexity of those listing actions; that
is, more complex actions generally are
more costly. For example, during the
past several years, the cost (excluding
publication costs) for preparing a 12–
month finding, without a proposed rule,
has ranged from approximately $11,000
for one species with a restricted range
and involving a relatively
uncomplicated analysis to $305,000 for
another species that is wide-ranging and
involving a complex analysis.
We cannot spend more than is
appropriated for the Listing Program
without violating the Anti-Deficiency
Act (see 31 U.S.C. § 1341(a)(1)(A)). In
addition, in FY 1998 and for each fiscal
year since then, Congress has placed a
statutory cap on funds that may be
expended for the Listing Program, equal
to the amount expressly appropriated
for that purpose in that fiscal year. This
cap was designed to prevent funds
appropriated for other functions under
the Act (for example, recovery funds for
removing species from the Lists), or for
other Service programs, from being used
for Listing Program actions (see House
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Report 105-163, 105th Congress, 1st
Session, July 1, 1997).
Recognizing that designation of
critical habitat for species already listed
would consume most of the overall
Listing Program appropriation, Congress
also put a critical habitat subcap in
place in FY 2002 and has retained it
each subsequent year to ensure that
some funds are available for other work
in the Listing Program: ‘‘The critical
habitat designation subcap will ensure
that some funding is available to
address other listing activities’’ (House
Report No. 107 - 103, 107th Congress, 1st
Session, June 19, 2001). In FY 2002 and
each year until FY 2006, the Service has
had to use virtually the entire critical
habitat subcap to address courtmandated designations of critical
habitat, and consequently none of the
critical habitat subcap funds have been
available for other listing activities. In
FY 2007, we were able to use some of
the critical habitat subcap funds to fund
proposed listing determinations for
high-priority candidate species. In FY
2009, while we were unable to use any
of the critical habitat subcap funds to
fund proposed listing determinations,
we did use some of this money to fund
the critical habitat portion of some
proposed listing determinations, so that
the proposed listing determination and
proposed critical habitat designation
could be combined into one rule,
thereby being more efficient in our
work. In FY 2010, we are using some of
the critical habitat subcap funds to fund
actions with statutory deadlines.
Thus, through the listing cap, the
critical habitat subcap, and the amount
of funds needed to address courtmandated critical habitat designations,
Congress and the courts have in effect
determined the amount of money
available for other listing activities.
Therefore, the funds in the listing cap,
other than those needed to address
court-mandated critical habitat for
already-listed species, set the limits on
our determinations of preclusion and
expeditious progress.
Congress also recognized that the
availability of resources was the key
element in deciding, when making a 12–
month petition finding, whether we
would prepare and issue a listing
proposal or instead make a ‘‘warranted
but precluded’’ finding for a given
species. The Conference Report
accompanying Public Law 97-304,
which established the current statutory
deadlines and the warranted-butprecluded finding, states (in a
discussion on 90–day petition findings
that by its own terms also covers 12–
month findings) that the deadlines were
‘‘not intended to allow the Secretary to
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delay commencing the rulemaking
process for any reason other than that
the existence of pending or imminent
proposals to list species subject to a
greater degree of threat would make
allocation of resources to such a petition
[that is, for a lower-ranking species]
unwise.’’
In FY 2010, expeditious progress is
that amount of work that can be
achieved with $10,471,000, which is the
amount of money that Congress
appropriated for the Listing Program
(that is, the portion of the Listing
Program funding not related to critical
habitat designations for species that are
already listed). However these funds are
not enough to fully fund all our courtordered and statutory listing actions in
FY 2010, so we are using $1,114,417 of
our critical habitat subcap funds in
order to work on all of our required
petition findings and listing
determinations. This brings the total
amount of funds we have for listing
action in FY 2010 to $11,585,417.
Starting in FY 2010, we are also using
our funds to work on listing actions for
foreign species since that work was
transferred from the Division of
Scientific Authority, International
Affairs Program to the Endangered
Species Program. Our process is to make
our determinations of preclusion on a
nationwide basis to ensure that the
species most in need of listing will be
addressed first and also because we
allocate our listing budget on a
nationwide basis. The $11,585,417 is
being used to fund work in the
following categories: compliance with
court orders and court-approved
settlement agreements requiring that
petition findings or listing
determinations be completed by a
specific date; section 4 (of the Act)
listing actions with absolute statutory
deadlines; essential litigation-related,
administrative, and listing programmanagement functions; and highpriority listing actions for some of our
candidate species. The allocations for
each specific listing action are identified
in the Service’s FY 2010 Allocation
Table (part of our administrative
record).
In FY 2007, we had more than 120
species with an LPN of 2, based on our
September 21, 1983, guidance for
assigning an LPN for each candidate
species (48 FR 43098). Using this
guidance, we assign each candidate an
LPN of 1 to 12, depending on the
magnitude of threats (high vs. moderate
to low), immediacy of threats (imminent
or nonimminent), and taxonomic status
of the species (in order of priority:
monotypic genus (a species that is the
sole member of a genus); species; or part
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of a species (subspecies, distinct
population segment, or significant
portion of the range)). The lower the
listing priority number, the higher the
listing priority (that is, a species with an
LPN of 1 would have the highest listing
priority).
To be more efficient in our listing
process, as we work on proposed rules
for these species in the next several
years, we are preparing multi-species
proposals when appropriate, and these
may include species with lower priority
if they overlap geographically or have
the same threats as a species with an
LPN of 2. In addition, available staff
resources are also a factor in
determining which high-priority species
are provided with funding. Finally,
proposed rules for reclassification of
threatened species to endangered are
lower priority, since as listed species,
they are already afforded the protection
of the Act and implementing
regulations.
Given the above-mentioned funding
constraints, the Service’s priority is to
work on: (1) listing determinations for
listing actions with absolute statutory,
court-ordered, or court-approved
deadlines, and final listing
determinations for those species that
have been proposed for listing; and (2)
candidate species and reclassifications
of other higher priority threatened
species (i.e., species with LPN of 1).
This work includes all the actions listed
in the tables below under expeditious
progress.
As explained above, a determination
that listing is warranted but precluded
must also demonstrate that expeditious
progress is being made to add or remove
qualified species to and from the Lists
of Endangered and Threatened Wildlife
and Plants. (Although we do not discuss
57727
it in detail here, we are also making
expeditious progress in removing
species from the list under the Recovery
program, which is funded by a separate
line item in the budget of the
Endangered Species Program. As
explained above in our description of
the statutory cap on Listing Program
funds, the Recovery Program funds and
actions supported by them cannot be
considered in determining expeditious
progress made in the Listing Program.)
As with our ‘‘precluded’’ finding,
expeditious progress in adding qualified
species to the Lists is a function of the
resources available and the competing
demands for those funds. Given that
limitation, we find that we made
progress in FY 2009 in the Listing
Program and will continue to make
progress in FY 2010. This progress
included preparing and publishing the
following determinations:
FY 2010 COMPLETED LISTING ACTIONS
Title
Actions
FR Pages
10/08/2009
Listing Lepidium papilliferum (Slickspot Peppergrass) as a Threatened Species Throughout Its Range
Final Listing
Threatened ............
74 FR 52013-52064
10/27/2009
90-day Finding on a Petition To List the American Dipper in the
Black Hills of South Dakota as Threatened or Endangered
Notice of 90–day
Petition Finding, .....
Not substantial .......
74 FR 55177-55180
10/28/2009
Status Review of Arctic Grayling (Thymallus arcticus) in the Upper
Missouri River System
Notice of Intent to
Conduct Status ......
Review ...................
74 FR 55524-55525
11/03/2009
Listing the British Columbia Distinct Population Segment of the
Queen Charlotte Goshawk Under the Endangered Species Act
Proposed Listing
Threatened ............
74 FR 56757-56770
11/03/2009
Listing the Salmon-Crested Cockatoo as Threatened Throughout
Its Range with Special Rule
Proposed Listing
Threatened
74 FR 56770-56791
11/23/2009
Status Review of Gunnison sage-grouse (Centrocercus minimus)
Notice of Intent to
Conduct Status
Review ...................
74 FR 61100-61102
12/03/2009
12-Month Finding on a Petition to List the Black-tailed Prairie Dog
as Threatened or Endangered
Notice of 12–month
petition finding, Not
warranted
74 FR 63343-63366
12/03/2009
90-Day Finding on a Petition to List Sprague’s Pipit as
Threatened or Endangered
Notice of 90–day
Petition Finding, .....
Substantial .............
74 FR 63337-63343
12/15/2009
90-Day Finding on Petitions To List Nine Species of Mussels
From Texas as Threatened or Endangered With Critical Habitat
Notice of 90–day
Petition Finding, .....
Substantial .............
74 FR 66260-66271
12/16/2009
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Publication Date
Partial 90-Day Finding on a Petition to List 475 Species in the
Southwestern United States as Threatened or Endangered With
Critical Habitat
Notice of 90–day
Petition Finding, .....
Not substantial and
Substantial .............
74 FR 66865-66905
12/17/2009
12–month Finding on a Petition To Change the Final Listing of the
Distinct Population Segment of the Canada Lynx To Include
New Mexico
Notice of 12–month
petition finding,
Warranted but
precluded ...............
74 FR 66937-66950
1/05/2010
Listing Foreign Bird Species in Peru and Bolivia as Endangered
Throughout Their Range
Proposed Listing
Endangered ...........
75 FR 605-649
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FY 2010 COMPLETED LISTING ACTIONS—Continued
Title
Actions
FR Pages
1/05/2010
Listing Six Foreign Birds as Endangered Throughout Their Range
Proposed Listing
Endangered ...........
75 FR 286-310
1/05/2010
Withdrawal of Proposed Rule to List Cook’s Petrel
Proposed rule,
withdrawal ..............
75 FR 310-316
1/05/2010
Final Rule to List the Galapagos Petrel and Heinroth’s Shearwater
as Threatened Throughout Their Ranges
Final Listing
Threatened ............
75 FR 235-250
1/20/2010
Initiation of Status Review for Agave eggersiana and Solanum
conocarpum
Notice of Intent to
Conduct Status
Review ...................
75 FR 3190-3191
2/09/2010
12–month Finding on a
Petition to List the American Pika as Threatened or Endangered
Notice of 12–month
petition finding, Not
warranted
75 FR 6437-6471
2/25/2010
12-Month Finding on a Petition To List the Sonoran Desert
Population of the Bald Eagle as a Threatened or Endangered
Distinct Population Segment
Notice of 12–month
petition finding, Not
warranted
75 FR 8601-8621
2/25/2010
Withdrawal of Proposed Rule To List the Southwestern
Washington/Columbia River Distinct Population Segment of
Coastal Cutthroat Trout (Oncorhynchus clarki clarki) as
Threatened
Withdrawal of
Proposed Rule to ..
List .........................
75 FR 8621-8644
3/18/2010
90-Day Finding on a Petition to List the Berry Cave Salamander
as Endangered
Notice of 90–day
Petition Finding, .....
Substantial .............
75 FR 13068-13071
3/23/2010
90-Day Finding on a Petition to List the Southern Hickorynut
Mussel (Obovaria jacksoniana) as Endangered or Threatened
Notice of 90–day
Petition Finding, .....
Not substantial .......
75 FR 13717-13720
3/23/2010
90-Day Finding on a Petition to List the Striped Newt as
Threatened
Notice of 90–day
Petition Finding, .....
Substantial .............
75 FR 13720-13726
3/23/2010
12-Month Findings for Petitions to List the Greater Sage-Grouse
(Centrocercus urophasianus)
as Threatened or Endangered
Notice of 12–month
petition finding,
Warranted but ........
precluded ...............
75 FR 13910-14014
3/31/2010
12-Month Finding on a Petition to List the Tucson Shovel-Nosed
Snake (Chionactis occipitalis klauberi) as Threatened or Endangered with Critical Habitat
Notice of 12–month
petition finding,
Warranted but ........
precluded ...............
75 FR 16050-16065
4/5/2010
90-Day Finding on a Petition To List Thorne’s Hairstreak Butterfly
as Threatened or Endangered
Notice of 90–day
Petition Finding, .....
Substantial .............
75 FR 17062-17070
4/6/2010
12–month Finding on a Petition To List the Mountain Whitefish in
the Big Lost River, Idaho, as Endangered or Threatened
Notice of 12–month
petition finding, Not
warranted
75 FR 17352-17363
4/6/2010
90-Day Finding on a Petition to List a Stonefly (Isoperla jewetti)
and a Mayfly (Fallceon eatoni) as Threatened or Endangered
with Critical Habitat
Notice of 90–day
Petition Finding, .....
Not substantial .......
75 FR 17363-17367
4/7/2010
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Publication Date
12-Month Finding on a Petition to Reclassify the Delta Smelt
From Threatened to Endangered Throughout Its Range
Notice of 12–month
petition finding,
Warranted but ........
precluded ...............
75 FR 17667-17680
4/13/2010
Determination of Endangered Status for 48 Species on Kauai and
Designation of Critical Habitat
Final Listing
Endangered ...........
75 FR 18959-19165
4/15/2010
Initiation of Status Review of the North American Wolverine in the
Contiguous United States
Notice of Initiation of
Status Review
75 FR 19591-19592
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57729
FY 2010 COMPLETED LISTING ACTIONS—Continued
Publication Date
Title
Actions
FR Pages
12-Month Finding on a Petition to List the Wyoming Pocket
Gopher as Endangered or Threatened with Critical Habitat
Notice of 12–month
petition finding, Not
warranted
75 FR 19592-19607
4/16/2010
90-Day Finding on a Petition to List a Distinct Population
Segment of the Fisher in Its United States Northern Rocky
Mountain Range as Endangered or Threatened with Critical
Habitat
Notice of 90–day
Petition Finding, .....
Substantial .............
75 FR 19925-19935
4/20/2010
Initiation of Status Review for Sacramento splittail (Pogonichthys
macrolepidotus)
Notice of Initiation of
Status Review
75 FR 20547-20548
4/26/2010
90-Day Finding on a Petition to List the Harlequin Butterfly as
Endangered
Notice of 90–day
Petition Finding, .....
Substantial .............
75 FR 21568-21571
4/27/2010
12-Month Finding on a Petition to List Susan’s Purse-making
Caddisfly (Ochrotrichia susanae) as Threatened or Endangered
Notice of 12–month
petition finding, Not
warranted
75 FR 22012-22025
4/27/2010
90–day Finding on a Petition to List the Mohave Ground Squirrel
as Endangered with Critical Habitat
Notice of 90–day
Petition Finding, .....
Substantial .............
75 FR 22063-22070
5/4/2010
90-Day Finding on a Petition to List Hermes Copper Butterfly as
Threatened or Endangered
Notice of 90–day
Petition Finding, .....
Substantial .............
75 FR 23654-23663
6/1/2010
90-Day Finding on a Petition To List Castanea pumila var.
ozarkensis
Notice of 90–day
Petition Finding, .....
Substantial .............
75 FR 30313-30318
6/1/2010
12–month Finding on a Petition to List the White-tailed Prairie
Dog as Endangered or Threatened
Notice of 12–month
petition finding, Not
warranted
75 FR 30338-30363
6/9/2010
90-Day Finding on a Petition To List van Rossem’s Gull-billed
Tern as Endangered orThreatened.
Notice of 90–day
Petition Finding, .....
Substantial .............
75 FR 32728-32734
6/16/2010
90-Day Finding on Five Petitions to List Seven Species of
Hawaiian Yellow-faced Bees as Endangered
Notice of 90–day
Petition Finding, .....
Substantial .............
75 FR 34077-34088
6/22/2010
12-Month Finding on a Petition to List the Least Chub as
Threatened or Endangered
Notice of 12–month
petition finding,
Warranted but ........
precluded ...............
75 FR 35398-35424
6/23/2010
90-Day Finding on a Petition to List the Honduran Emerald
Hummingbird as Endangered
Notice of 90–day
Petition Finding, .....
Substantial .............
75 FR 35746-35751
6/23/2010
Listing Ipomopsis polyantha (Pagosa Skyrocket) as Endangered
Throughout Its Range, and Listing Penstemon debilis
(Parachute Beardtongue) and Phacelia submutica (DeBeque
Phacelia) as Threatened Throughout Their Range
Proposed Listing
Endangered ...........
Proposed Listing ....
Threatened ............
75 FR 35721-35746
6/24/2010
Listing the Flying Earwig Hawaiian Damselfly and Pacific
Hawaiian Damselfly As Endangered Throughout Their Ranges
Final Listing
Endangered ...........
75 FR 35990-36012
6/24/2010
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4/15/2010
Listing the Cumberland Darter, Rush Darter, Yellowcheek Darter,
Chucky Madtom, and Laurel Dace as Endangered Throughout
Their Ranges
Proposed Listing
Endangered ...........
75 FR 36035-36057
6/29/2010
Listing the Mountain Plover as Threatened
Reinstatement of
Proposed Listing ....
Threatened ............
75 FR 37353-37358
7/20/2010
90-Day Finding on a Petition to List Pinus albicaulis (Whitebark
Pine) as Endangered or Threatened with Critical Habitat
Notice of 90–day
Petition Finding, .....
Substantial .............
75 FR 42033-42040
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Federal Register / Vol. 75, No. 183 / Wednesday, September 22, 2010 / Proposed Rules
FY 2010 COMPLETED LISTING ACTIONS—Continued
Title
Actions
FR Pages
7/20/2010
12-Month Finding on a Petition to List the Amargosa Toad as
Threatened or Endangered
Notice of 12–month
petition finding, Not
warranted
75 FR 42040-42054
7/20/2010
90-Day Finding on a Petition to List the Giant Palouse Earthworm
(Driloleirus americanus) as Threatened or Endangered
Notice of 90–day
Petition Finding, .....
Substantial .............
75 FR 42059-42066
7/27/2010
Determination on Listing the Black-Breasted Puffleg as
Endangered Throughout its Range; Final Rule
Final Listing
Endangered ...........
75 FR 43844-43853
7/27/2010
Final Rule to List the Medium Tree-Finch (Camarhynchus pauper)
as Endangered Throughout Its Range
Final Listing
Endangered ...........
75 FR 43853-43864
8/3/2010
Determination of Threatened Status for Five Penguin Species
Final Listing
Threatened ............
75 FR 45497- 45527
8/4/2010
90-Day Finding on a Petition To List the Mexican Gray Wolf as an
Endangered Subspecies With Critical Habitat
Notice of 90–day
Petition Finding, .....
Substantial .............
75 FR 46894- 46898
8/10/2010
90-Day Finding on a Petition to List Arctostaphylos franciscana as
Endangered with Critical Habitat
Notice of 90–day
Petition Finding, .....
Substantial .............
75 FR 48294-48298
8/17/2010
Listing Three Foreign Bird Species from Latin America and the
Caribbean as Endangered Throughout Their Range
Final Listing
Endangered ...........
75 FR 50813-50842
8/17/2010
90-Day Finding on a Petition to List Brian Head Mountainsnail as
Endangered or Threatened with Critical Habitat
Notice of 90–day
Petition Finding, .....
Not substantial .......
75 FR 50739-50742
8/24/2010
90-Day Finding on a Petition to List the Oklahoma Grass
Pink Orchid as Endangered or Threatened .................................
Notice of 90–day
Petition Finding, .....
Substantial .............
75 FR 51969-51974
9/01/2010
12-Month Finding on a Petition to List the White-Sided Jackrabbit
as Threatened or Endangered
Notice of 90–day
Notice of 12-month
petition finding,.
Not warranted ........
75 FR 53615-53629
9/08/2010
Proposed Rule To List the Ozark Hellbender Salamander as
Endangered ..................................................................................
Proposed
ListingEndangered
75 FR 54561-54579
9/08/2010
Revised 12-Month Finding to List the Upper Missouri River
Distinct Population Segment of Arctic Grayling as Endangered
or Threatened ...............................................................................
Notice of 12-month
petition finding,
Warranted but
precluded ...............
75 FR 54707-54753
9/09/2010
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Publication Date
12-Month Finding on a Petition to List the Jemez Mountains
Salamander (Plethodon neomexicanus) as Endangered or ........
Threatened with Critical Habitat ...................................................
Notice of 12-month
petition finding,
Warranted but ........
precluded ...............
75 FR 54822-54845
Our expeditious progress also
includes work on listing actions that we
funded in FY 2010 but have not yet
been completed to date. These actions
are listed below. Actions in the top
section of the table are being conducted
under a deadline set by a court. Actions
in the middle section of the table are
being conducted to meet statutory
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timelines, that is, timelines required
under the Act. Actions in the bottom
section of the table are high-priority
listing actions. These actions include
work primarily on species with an LPN
of 2, and selection of these species is
partially based on available staff
resources, and when appropriate,
include species with a lower priority if
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they overlap geographically or have the
same threats as the species with the
high priority. Including these species
together in the same proposed rule
results in considerable savings in time
and funding, as compared to preparing
separate proposed rules for each of them
in the future.
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Federal Register / Vol. 75, No. 183 / Wednesday, September 22, 2010 / Proposed Rules
Actions funded in FY 2010 but not yet completed
Species
Action
Actions Subject to Court Order/Settlement Agreement
6 Birds from Eurasia
Final listing determination
African penguin
Final listing determination
Flat-tailed horned lizard
Final listing determination
Mountain plover
Final listing determination
6 Birds from Peru
Proposed listing determination
Sacramento splittail
Proposed listing determination
Pacific walrus
12–month petition finding
Gunnison sage-grouse
12–month petition finding
Wolverine
12–month petition finding
Solanum conocarpum
12–month petition finding
Sprague’s pipit
12–month petition finding
Desert tortoise – Sonoran population
12–month petition finding
Pygmy rabbit (rangewide)1
12–month petition finding
Thorne’s Hairstreak Butterfly
12–month petition finding
Hermes copper butterfly
12–month petition finding
Actions with Statutory Deadlines
Casey’s june beetle
Final listing determination
Georgia pigtoe, interrupted rocksnail, and rough hornsnail
Final listing determination
7 Bird species from Brazil
Final listing determination
Southern rockhopper penguin – Campbell Plateau population
Final listing determination
5 Bird species from Colombia and Ecuador
Final listing determination
Queen Charlotte goshawk
Final listing determination
5 species southeast fish (Cumberland darter, rush darter, yellowcheek darter, chucky madtom,
and laurel dace)
Final listing determination
Salmon crested cockatoo
Proposed listing determination
CA golden trout
12–month petition finding
Black-footed albatross
12–month petition finding
Mount Charleston blue butterfly
12–month petition finding
Mojave fringe-toed lizard1
12–month petition finding
Kokanee – Lake Sammamish
population1
12–month petition finding
12–month petition finding
Northern leopard frog
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Cactus ferruginous pygmy-owl1
12–month petition finding
Tehachapi slender salamander
12–month petition finding
Coqui Llanero
12–month petition finding
Dusky tree vole
12–month petition finding
3 MT invertebrates (mist forestfly(Lednia tumana), Oreohelix sp.3, Oreohelix sp. 31) from 206
species petition
12–month petition finding
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Federal Register / Vol. 75, No. 183 / Wednesday, September 22, 2010 / Proposed Rules
Actions funded in FY 2010 but not yet completed
Species
Action
5 UT plants (Astragalus hamiltonii, Eriogonum soredium, Lepidium ostleri, Penstemon flowersii,
Trifolium friscanum) from 206 species petition
12–month petition finding
2 CO plants (Astragalus microcymbus, Astragalus schmolliae) from 206 species petition
12–month petition finding
5 WY plants (Abronia ammophila, Agrostis rossiae, Astragalus proimanthus, Boechere (Arabis)
pusilla, Penstemon gibbensii) from 206 species petition
12–month petition finding
Leatherside chub (from 206 species petition)
12–month petition finding
Frigid ambersnail (from 206 species petition)
12–month petition finding
Gopher tortoise – eastern population
12–month petition finding
Wrights marsh thistle
12–month petition finding
67 of 475 southwest species
12–month petition finding
Grand Canyon scorpion (from 475 species petition)
12–month petition finding
Anacroneuria wipukupa (a stonefly from 475 species petition)
12–month petition finding
Rattlesnake-master borer moth (from 475 species petition)
12–month petition finding
3 Texas moths (Ursia furtiva, Sphingicampa blanchardi, Agapema galbina) (from 475 species
petition)
12–month petition finding
2 Texas shiners (Cyprinella sp., Cyprinella lepida) (from 475 species petition)
12–month petition finding
3 South Arizona plants (Erigeron piscaticus, Astragalus hypoxylus, Amoreuxia gonzalezii) (from
475 species petition)
12–month petition finding
5 Central Texas mussel species (3 from 475 species petition)
12–month petition finding
14 parrots (foreign species)
12–month petition finding
Berry Cave salamander1
12–month petition finding
Striped Newt1
12–month petition finding
Fisher – Northern Rocky Mountain
Range1
12–month petition finding
Mohave Ground Squirrel1
12–month petition finding
Puerto Rico Harlequin Butterfly
12–month petition finding
Western gull-billed tern
12–month petition finding
Ozark chinquapin (Castanea pumila var. ozarkensis)
12–month petition finding
HI yellow-faced bees
12–month petition finding
Giant Palouse earthworm
12–month petition finding
Whitebark pine
12–month petition finding
OK grass pink (Calopogon oklahomensis)1
12–month petition finding
Southeastern pop snowy plover & wintering pop. of piping
plover1
90–day petition finding
90–day petition finding
Smooth-billed ani1
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Eagle Lake trout1
90–day petition finding
Bay Springs
salamander1
90–day petition finding
32 species of snails and slugs1
90–day petition finding
42 snail species (Nevada & Utah)
90–day petition finding
Red knot roselaari subspecies
90–day petition finding
Peary caribou
90–day petition finding
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57733
Actions funded in FY 2010 but not yet completed
Species
Action
Plains bison
90–day petition finding
Spring Mountains checkerspot butterfly
90–day petition finding
Spring pygmy sunfish
90–day petition finding
Bay skipper
90–day petition finding
Unsilvered fritillary
90–day petition finding
Texas kangaroo rat
90–day petition finding
Spot-tailed earless lizard
90–day petition finding
Eastern small-footed bat
90–day petition finding
Northern long-eared bat
90–day petition finding
Prairie chub
90–day petition finding
10 species of Great Basin butterfly
90–day petition finding
6 sand dune (scarab) beetles
90–day petition finding
Golden-winged warbler
90–day petition finding
Sand-verbena moth
90–day petition finding
Aztec (beautiful) gilia
90–day petition finding
Arapahoe snowfly
90–day petition finding
404 Southeast species
90–day petition finding
High Priority Listing Actions3
19 Oahu candidate species3 (16 plants, 3 damselflies) (15 with LPN = 2, 3 with LPN = 3, 1 with
LPN =9)
Proposed listing
19 Maui-Nui candidate species3 (16 plants, 3 tree snails) (14 with LPN = 2, 2 with LPN = 3, 3 with
LPN = 8)
Proposed listing
Sand dune lizard3 (LPN = 2)
Proposed listing
2 Arizona springsnails3 (Pyrgulopsis bernadina (LPN = 2), Pyrgulopsis trivialis (LPN = 2))
Proposed listing
2 New Mexico springsnails3 (Pyrgulopsis chupaderae (LPN = 2), Pyrgulopsis thermalis (LPN =
11))
Proposed listing
2 mussels3 (rayed bean (LPN = 2), snuffbox No LPN)
Proposed listing
2 mussels3 (sheepnose (LPN = 2), spectaclecase (LPN = 4),)
Proposed listing
Altamaha
spinymussel3
(LPN = 2)
Proposed listing
8 southeast mussels (southern kidneyshell (LPN = 2), round ebonyshell (LPN = 2), Alabama
pearlshell (LPN = 2), southern sandshell (LPN = 5), fuzzy pigtoe (LPN = 5), Choctaw bean (LPN
= 5), narrow pigtoe (LPN = 5), and tapered pigtoe (LPN = 11))
Proposed listing
1
Funds for listing actions for these species were provided in previous FYs.
We funded a proposed rule for this subspecies with an LPN of 3 ahead of other species with LPN of 2, because the threats to the species
were so imminent and of a high magnitude that we considered emergency listing if we were unable to fund work on a proposed listing rule in FY
2008.
3 Funds for these high-priority listing actions were provided in FY 2008 or 2009
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2
We endeavored to make our listing
actions as efficient and timely as
possible, given the requirements of the
relevant law and regulations, and
constraints relating to workload and
personnel. We are continually
considering ways to streamline
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processes or achieve economies of scale,
such as by batching related actions
together. Given our limited budget for
implementing section 4 of the Act, these
actions described above collectively
constitute expeditious progress.
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We intend that any proposed
reclassification of Agave eggersiana will
be as accurate as possible. Therefore, we
will continue to accept additional
information and comments from all
concerned governmental agencies, the
scientific community, industry, or any
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Federal Register / Vol. 75, No. 183 / Wednesday, September 22, 2010 / Proposed Rules
other interested party concerning this
finding.
Agave eggersiana will be added to the
list of candidate species upon
publication of this 12–month finding.
We will continue to evaluate this
species as new information becomes
available. This review will determine if
a change in status is warranted,
including the need to make prompt use
of emergency listing procedures.
References Cited
A complete list of references cited is
available on the Internet at https://
www.regulations.gov and upon request
from the Caribbean Ecological Services
Field Office (see ADDRESSES section).
Author(s)
The primary authors of this notice are
the staff members of the Caribbean
Ecological Services Field Office.
Authority
The authority for this section is
section 4 of the Endangered Species Act
of 1973, as amended (16 U.S.C. 1531 et
seq.).
Dated: September 2, 2010.
Paul R. Schmidt,
Acting Director, Fish and Wildlife Service.
[FR Doc. 2010–23571 Filed 9–21–10; 8:45 am]
BILLING CODE 4310–55–S
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 622
RIN 0648–AY11
Fisheries of the Caribbean, Gulf of
Mexico, and South Atlantic; SnapperGrouper Fishery off the Southern
Atlantic States; Amendment 17B
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Notice of Availability of
Amendment 17B to South Atlantic
Snapper-Grouper Fishery Management
Plan; request for comments.
AGENCY:
The South Atlantic Fishery
Management Council (Council) has
submitted Amendment 17B to the
Fishery Management Plan for the
Snapper-Grouper Fishery of the South
Atlantic Region (FMP) for review,
approval, and implementation by
NMFS. The amendment proposes
actions to specify annual catch limits
(ACLs), and accountability measures
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SUMMARY:
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17:41 Sep 21, 2010
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(AMs) for nine snapper-grouper species,
eight of which are undergoing
overfishing; specify recreational and
commercial allocations for golden
tilefish; modify management measures
to limit total mortality of each species
to their respective ACLs; and add ACLs,
ACTs, and AMs to the management
measures that may be amended via the
framework procedure. The actions
contained in Amendment 17B are
intended to address overfishing of eight
snapper-grouper species while
maintaining catch levels consistent with
achieving optimum yield for all nine
species included in the amendment.
DATES: Comments must be received no
later than 5 p.m., eastern time, on
November 22, 2010.
ADDRESSES: You may submit comments,
identified by ‘‘0648–AY11’’, by any one
of the following methods:
• Electronic Submissions: Submit all
electronic public comments via the
Federal e-Rulemaking Portal https://
www.regulations.gov
• Fax: 727–824–5308, Attn: Kate
Michie
• Mail: Kate Michie, Southeast
Regional Office, NMFS, 263 13th
Avenue South, St. Petersburg, FL 33701
Instructions: No comments will be
posted for public viewing until after the
comment period is over. All comments
received are a part of the public record
and will generally be posted to https://
www.regulations.gov without change.
All Personal Identifying Information (for
example, name, address, etc.)
voluntarily submitted by the commenter
may be publicly accessible. Do not
submit Confidential Business
Information or otherwise sensitive or
protected information.
To submit comments through the
Federal e–Rulemaking Portal: https://
www.regulations.gov, enter ‘‘NOAA–
NMFS–2010–0091’’ in the keyword
search, then check the box labeled
(Select to find documents accepting
comments or submissions(, then select
(Send a Comment or Submission.(
NMFS will accept anonymous
comments (enter N/A in the required
fields, if you wish to remain
anonymous). Attachments to electronic
comments will be accepted in Microsoft
Word, Excel, WordPerfect, or Adobe
PDF file formats only.
Copies of Amendment 17B may be
obtained from the South Atlantic
Fishery Management Council, 4055
Faber Place, Suite 201, North
Charleston, SC 29405; phone: 843–571–
4366 or 866–SAFMC–10 (toll free); fax:
843–769–4520; e-mail:
safmc@safmc.net. Amendment 17B
includes an Environmental Assessment,
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an Initial Regulatory Flexibility
Analysis, a Regulatory Impact Review,
and a Social Impact Assessment/Fishery
Impact Statement.
FOR FURTHER INFORMATION CONTACT: Kate
Michie, telephone: 727–824–5305; fax:
727–824–5308; e-mail:
Kate.Michie@noaa.gov.
SUPPLEMENTARY INFORMATION: The South
Atlantic snapper-grouper fishery is
managed under the FMP. The FMP was
prepared by the Council and
implemented by NMFS under the
authority of the Magnuson-Stevens
Fishery Conservation and Management
Act (Magnuson-Stevens Act) by
regulations at 50 CFR part 622.
Background
Revisions to the Magnuson–Stevens
Act in 2006 require that if a stock or
stock complex in an FMP is undergoing
overfishing, the FMP must establish by
2010 a mechanism for specifying ACLs
at a level that prevents overfishing and
does not exceed the fishing level
recommendations of the respective
Council(s Scientific and Statistical
Committee or other established peer
review processes. The MagnusonStevens Act also requires that NMFS
implement measures to ensure
accountability to prevent an ACL from
being exceeded or correcting for an ACL
overage if one should occur. The
National Standard 1 Guidelines,
published on January 16, 2009 (74 FR
3178), provide guidance for establishing
ACLs and AMs in our nation’s fisheries.
In the South Atlantic snapper-grouper
fishery there are nine species currently
undergoing overfishing including:
speckled hind, warsaw grouper, snowy
grouper, golden tilefish, black sea bass,
red grouper, gag, vermilion snapper, and
red snapper. Amendment 17B includes
actions to establish ACLs and AMs for
eight of these species as well as black
grouper. Actions to address red snapper
overfishing are contained in a separate
amendment (Amendment 17A).
An ACL is the level of annual catch
of a stock or stock complex that if met
or exceeded serves as the basis for
triggering an AM. The Magnuson–
Stevens Act requires ACLs be set at
levels that prevent overfishing from
occurring. ACLs may incorporate
management and scientific uncertainty,
and take into account the amount of
data available and level of vulnerability
to overfishing for each species. Separate
ACLs may be established for each sector
of a fishery, i.e., commercial and
recreational. However, the combined
total of all sector ACLs may not exceed
the total ACL for a species or species
complex.
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Agencies
[Federal Register Volume 75, Number 183 (Wednesday, September 22, 2010)]
[Proposed Rules]
[Pages 57720-57734]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2010-23571]
=======================================================================
-----------------------------------------------------------------------
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[Docket number FWS-R4-ES-2010-0051]
[MO 92210-0-0008-B2]
Endangered and Threatened Wildlife and Plants; 12-Month Finding
on a Petition to List Agave eggersiana (no common name) as Endangered
AGENCY: Fish and Wildlife Service, Interior.
ACTION: Notice of 12-month petition finding.
-----------------------------------------------------------------------
SUMMARY: We, the Fish and Wildlife Service (Service), announce a 12-
month finding on a petition to list the plant Agave eggersiana (no
common name) as endangered under the Endangered Species Act of 1973, as
amended (Act). After review of all available scientific and commercial
information, we find that listing A. eggersiana is warranted.
Currently, however, listing A. eggersiana is precluded by higher
priority actions to amend the Lists of Endangered and Threatened
Wildlife and Plants. Upon publication of this 12-month petition
finding, we will add A. eggersiana to our candidate species list. We
will develop a proposed rule to list A. eggersiana as our priorities
allow. We will make any determination on critical habitat during
development of the proposed listing rule. In any interim period the
status of the candidate taxon will be addressed through our annual
Candidate Notice of Review (CNOR).
DATES: The finding announced in this document was made on September 22,
2010.
ADDRESSES: This finding is available on the Internet at https://www.regulations.gov at Docket Number [FWS-R4-ES-2010-0051]. Supporting
documentation we used in preparing this finding is available for public
inspection, by appointment, during normal business hours at the U.S.
Fish and Wildlife Service, Caribbean Ecological Services Field Office,
Road 301, Km. 5.1, Boquero[acute]n, Puerto Rico 00622. Please submit
any new information, materials, comments, or questions concerning this
species or this finding to the above internet address or the mailing
address listed under FOR FURTHER INFORMATION CONTACT.
FOR FURTHER INFORMATION CONTACT: Ms. Marelisa Rivera, Assistant Field
Supervisor, Caribbean Ecological Services Field Office, P.O. Box 491,
Boquero[acute]n, Puerto Rico 00622; by telephone at (787) 851-7297; or
by facsimile at (787) 851-7440. Persons who use a telecommunications
device for the deaf (TDD) may call the Federal Information Relay
Service (FIRS) at 800-877-8339.
Background
Section 4(b)(3)(A) of the Act (16 U.S.C. 1531 et seq.) requires
that, for any petition to revise the Federal Lists of Threatened and
Endangered Wildlife and Plants that contains substantial scientific or
commercial information that listing a species may be warranted, we make
a finding within 12 months of the date of receipt of the petition. In
this finding, we determine whether the petitioned action is: (a) Not
warranted, (b) warranted, or (c) warranted, but immediate proposal of a
regulation implementing the petitioned action is precluded by other
pending proposals to determine whether species are threatened or
endangered, and expeditious progress is being made to add or remove
qualified species from the Federal Lists of Endangered and Threatened
Wildlife and Plants. Section 4(b)(3)(C) of the Act requires that we
treat a petition for which the requested action is found to be
warranted but precluded as though resubmitted on the date of such
finding, that is, requiring a subsequent finding to be made within 12
months. We must publish these 12-month findings in the Federal
Register.
[[Page 57721]]
Previous Federal Actions
We identified Agave eggersiana as a category 2 candidate species in
the Notice of Review published in the Federal Register on September 30,
1993 (58 FR 51144) and subsequent publication. A category 2 species was
one for which the Service had information that proposing as endangered
or threatened may be appropriate but for which sufficient information
was not currently available to support a proposed rule. Designation of
category 2 species was discontinued in the February 28, 1996, Notice of
Review (61 FR 7596). This notice redefined candidates to include only
species for which we have information needed to propose them for
listing, and as a result, Agave eggersiana was removed from the
Candidate species list.
On November 21, 1996, we received a petition from the U.S. Virgin
Islands Department of Planning and Natural Resources (DPNR) requesting
that we list Agave eggersiana and Solanum conocarpum as endangered. On
November 16, 1998, we published in the Federal Register (63 FR 63659)
our finding that the petition to list A. eggersiana and S. conocarpum
presented substantial information indicating that the requested action
may be warranted and initiated a status review on these two plants. On
September 1, 2004, the Center for Biological Diversity filed a lawsuit
against the Department of the Interior and the U.S. Fish and Wildlife
Service (Service) alleging that the Service failed to publish a 12-
month finding for A. eggersiana and S. conocarpum (Center for
Biological Diversity v. Norton, Civil Action No. 1:04-CV-2553 CAP). In
a stipulated settlement agreement resolving that case, signed April 27,
2005, we agreed to submit our 12-month finding for A. eggersiana and S.
conocarpum to the Federal Register by February 28, 2006. On March 7,
2006, we published our 12-month finding (71 FR 11367) that listing of
A. eggersiana and S. conocarpum was not warranted. On September 9,
2008, the Center for Biological Diversity filed a complaint challenging
our 12-month finding (Center for Biological Diversity v. Hamilton, Case
No. 1:08-cv-02830 -CAP). In a settlement agreement approved by the
Court on August 21, 2009, the Service agreed to submit to the Federal
Register a new 12-month finding for A. eggersiana by September 17,
2010. This notice constitutes the 12-month finding on the 1996 petition
to list A. eggersiana as endangered.
Species Information
Taxonomy and Species Description
Agave eggersiana is a flowering plant of the family Agavaceae
(century plant family) endemic to the island of St. Croix in the U.S.
Virgin Islands. A. eggersiana was originally described in 1913 by
Trelease from material collected on St. Croix, and is distinguished
from other members of the Agavaceae family by its acaulescent (without
an evident leafy stem), non-suckering growth habit (vegetative
reproduction that does not form offshoots around its base), and fleshy,
nearly straight leaves with small marginal prickles (1.00 millimeter
(mm); 0.04 inches (in) long) that are nearly straight (Britton and
Wilson 1923, p. 156; Proctor and Acevedo-Rodri[acute]guez 2005, p.
118). Its flowers are deep yellow, 5 to 6 centimeters (cm) (1.95 to
2.34 in) long. After flowering, the panicles (inflorescence) produce
numerous small vegetative bulbs (bulbils), from which the species can
be propagated (Proctor and Acevedo-Rodri[acute]guez 2005, p. 118).
Avave eggersiana is not known to produce fruit. Furthermore, based on
observations of cultivated plants, Agave eggersiana requires at least
10 to 15 years to develop as a mature individual and to produce an
inflorescence (David Hamada, St. George Botanical Garden, 2010, pers.
comm.). Avave eggersiana like other Agave species are monocarpic,
meaning the plant dies after producing the spike or inflorescence.
Habitat and Distribution
Britton and Wilson (1923, p. 156) reported the species from
hillsides and plains in the eastern dry districts of St. Croix but did
not provide population estimates. In addition, Agave eggersiana is
cultivated on St. Croix and St. Thomas for ornament (Trelease 1913, p.
28; Britton and Wilson 1923, p. 156; Proctor and Acevedo-
Rodri[acute]guez 2005, p. 118). Information provided in the petition
(Kojis and Boulon, DPNR, 1996, pers. comm.) specified that the species
was last observed growing in the wild around 1984 to 1986 on St. Croix.
In 2003, DPNR stated that the species is believed to be extinct
(Plaskett 2003, pers. comm.; Dalmida-Smith 2010, pers. comm.). Proctor
and Acevedo-Rodri[acute]guez (2005, p. 118) provided a general
description of the species and they state that the species ``now
appears to be extinct in the wild.'' However, no citations or survey
information were provided to support this statement. Subsequently, in
2010, DPNR provided information based on field visits and reported the
existence of several populations in St. Croix (Dalmida-Smith 2010,
pers. comm.).
Current Status
Historically, Agave eggersiana was reported from the north coast in
Christiansted, St. Croix and along the south coast of the island. The
current distribution and rarity of the species do not represent the
historical range. Historically, sugar cane was the main crop on the
island and dominated the economy for nearly 200 years (Shaw, 1933, p.
414). Apparently, the former land use of the areas used for sugar cane
cultivation resulted in degradation of the species' habitat and nearly
extirpated the species from the wild. Sugarcane is no longer cultivated
on the island and the majority of the areas formerly used for sugarcane
plantations are currently grasslands and early secondary forests
dominated by the exotic tree Leucaena leucocephala (tantan).
In 2010, the Division of Fish and Wildlife of the DPNR (Dalmida-
Smith 2010, pers. comm.) conducted a local status review to determine
the extent of the populations of Agave eggersiana in St. Croix. They
reported five sites where the species was found; however, it is
uncertain if these populations are natural populations (individuals
that come from wild populations) or if the populations consist of
individuals that escaped from landscaping. The five reported sites are:
(1) Manchineel/ Ha'penny Beach (Southern St. Croix) with an estimated
30 individuals, which is approximately half the number of individuals
that they encountered 2 years before; (2) West side of Vagthus point
(Southern St. Croix ) with a single individual; (3) Gallows Bay
(Northern St. Croix) with several plants but no approximate number was
mentioned; (4) Protestant Cay (Northern St. Croix) with an estimated 30
individuals, including a number of young plants; and (5) Ruth Island
(Southern St. Croix) with a single individual that was introduced to
the cay many years ago. However, the exact year of this introduction is
unknown.
In February 2010, Service biologists conducted surveys of Agave
eggersiana on St. Croix. In their 2010 surveys, Service biologists
visited seven of the ten currently known populations (Table 1). They
did not survey the two areas where a single individual has been
reported (Ruth Island and West Vagthus point) or Buck Island Reef
National Monument, where individuals have been planted and recent
survey information exists. Based on their characteristics (growing
mixed with native vegetation, evidence of natural recruitment and the
presence of
[[Page 57722]]
different size classes), these surveys indicate that the species
currently occurs in six areas that appear to be remnants of wild
populations. Four localities (Buck Island Reef National Monument, Salt
River Bay, Ruth Island, and Lagoon Picnic Area) contain individuals
that were planted in recent years.
Table 1. Currently known populations of Agave eggersiana on St. Croix.
----------------------------------------------------------------------------------------------------------------
Estimated of
Locality Category Adult Individuals Source of Information
----------------------------------------------------------------------------------------------------------------
Manchineel / Ha'penny Beach Wild 25-30 Dalmida-Smith 2010,
pers. comm.; Monsegur
and Vargas 2010,
unpublished data
----------------------------------------------------------------------------------------------------------------
West Vagthus point Wild 1 Dalmida-Smith 2010.
pers. comm.
----------------------------------------------------------------------------------------------------------------
Gallows Bay Wild 2-3 David Hamada. 2010,
pers. comm.; Monsegur
and Vargas 2010,
unpublished data.
----------------------------------------------------------------------------------------------------------------
Protestant Cay Wild 30-51 + 60 bulbils Dalmida-Smith 2010,
pers. comm.; Monsegur
and Vargas 2010,
unpublished data
----------------------------------------------------------------------------------------------------------------
Ruth Island Introduced* 1 Dalmida-Smith 2010,
pers. comm.
----------------------------------------------------------------------------------------------------------------
Great Pond Wild 76 + 50 bulbils Monsegur and Vargas
2010, unpublished
data; Plaskett 2003.
pers. comm.
----------------------------------------------------------------------------------------------------------------
South Shore Wild 100 + 150 bulbils Monsegur and Vargas
2010, unpublished
data.
----------------------------------------------------------------------------------------------------------------
Salt River Bay Introduced** 6 Monsegur and Vargas
2010, unpublished
data.
----------------------------------------------------------------------------------------------------------------
Buck Island National Monument Introduced* 5 Monsegur and Vargas
2010, unpublished
data.
----------------------------------------------------------------------------------------------------------------
Lagoon Picnic Area Landscape 177 Monsegur and Vargas
2010, unpublished
data.
----------------------------------------------------------------------------------------------------------------
Total 450 +260 bulbils .......................
----------------------------------------------------------------------------------------------------------------
* Introduced by DPNR for conservation.
** Introduced by NPS for education and outreach.
The eight localities containing multiple Agave eggersiana plants
are described as follows:
(1) Gallows Bay (private property) has several individuals that are
considered by local experts as a remnant of a natural population (David
Hamada 2010, pers. comm.). Historical documents and illustrations show
that Agave eggersiana was common on the landscape of Gallows Bay (David
Hamada 2010, pers. comm.).
(2) Protestant Cay (owned by the government but leased to a private
party), has an estimated population of 51 adult individuals of
different sizes and about 60 bulbils.
(3) Ha'penny Beach (private property), has an estimated population
of 25 individuals of different size classes; one of the plants was
found flowering during the site visit conducted by the Service in 2010.
(4) Great Pond (managed by the Department of Housing, Parks and
Recreation) has a healthy population of A. eggersiana with different
size plants and evidence of recent flowering events. This population is
located near Great Pond, an area where it was suspected that
descendants from wild plants may have existed (Plaskett 2003, pers.
comm.).
(5) South Shore (private property), has a population of about 100
adult individuals and about 150 bulbils, all growing on small terraces
at a rocky cliff. This population is actively flowering and it was
noted that some of the bulbils are reaching the sea, suggesting a
possible dispersal mechanism for the species.
(6) Salt River Bay National Historic Park and Ecological Preserve
(SARI) (managed by the National Park Service (NPS)) has six individual
plants. In 2007, personnel from the NPS planted these individuals at
Salt River as part of the landscape with the idea of establishing a
population at the site and for outreach purposes. At the time of the
survey, five of these plants were producing spikes and were expected to
produce bulbils within the following months (Monsegur and Vargas,
USFWS, 2010, unpublished data). Based on information provided by
personnel from NPS, additional propagation efforts with the species are
planned in the near future (Lundgreen 2010, pers. comm.).
(7) Buck Island Reef National Monument (managed by the NPS) has an
estimated population of five individuals. In 2007, personnel from NPS
planted these five individuals on the island, but at present time there
is no information regarding the breeding condition of these plants
(Lundgreen 2010, pers. comm.).
(8) Lagoon Picnic Area (a public beach area that seems to be under
a reforestation effort funded by the Antilitter and Beautification
Commission) harbors about 177 plants as part of the landscape. The size
of the individuals in this area ranges from small planted bulbils to a
few adult individuals ready to flower. Based on the information
gathered and observations, about 450 adult individuals and 260 bulbils
are currently known in 10 localities, including 6 populations that are
considered wild, 3 introduced populations for conservation and public
education, and 1 landscape population (Table 1). In addition to these
localities, Monsegur and Vargas (2010, personal observation) documented
the species presence in private gardens scattered throughout the
island. We estimate about 90 adult individuals are present in these
private gardens.
At the present time, information on ecology, phenology, and
genetics for Agave eggersiana is lacking. Samples of A. eggersiana from
individuals in the Gallows Bay area have been collected for genetics
analysis, but results were not available prior to making this finding
(Ray 2010, pers. comm.).
[[Page 57723]]
Current evidence suggests that the wild and cultivated populations
have minimum genetic variation. Therefore, all A. eggersiana plants
(cultivated and wild) are included as part of the listable entity in
this finding; however, we have focused our assessment of threats to the
wild populations. Although data suggest that cultivated individuals
could be used as genetic stock to aid in the long-term survival of this
species, most cultivated populations are groomed to prevent recruitment
and thus offer minimal conservation contribution. We do not feel that
cultivated individuals propagated for private or commercial uses aid in
the conservation or the recovery of the species in the wild.
Summary of Information Pertaining to the Five Factors
Section 4 of the Act (16 U.S.C. 1533), and implementing regulations
(50 CFR 424), set forth procedures for adding species to the Federal
Lists of Endangered and Threatened Wildlife and Plants. Under section
4(a)(1) of the Act, a species may be determined to be endangered or
threatened based on any of the following five factors: (A) The present
or threatened destruction, modification, or curtailment of its habitat
or range; (B) overutilization for commercial, recreational, scientific,
or educational purposes; (C) disease or predation; (D) the inadequacy
of existing regulatory mechanisms; or (E) other natural or manmade
factors affecting its continued existence. In making this finding,
information pertaining to Agave eggersiana, in relation to the five
factors provided in section 4(a)(1) of the Act is discussed below.
In considering what factors might constitute threats to a species,
we must look beyond the exposure of the species to a factor to evaluate
whether the species may respond to the factor in a way that causes
actual impacts to the species. If there is exposure to a factor and the
species responds negatively, the factor may be a threat and we attempt
to determine how significant a threat it is. The threat is significant
if it drives, or contributes to, the risk of extinction of the species
such that the species warrants listing as endangered or threatened as
those terms are defined in the Act.
Factor A: The Present or Threatened Destruction, Modification, or
Curtailment of the Species' Habitat or Range
Of the currently known populations, only three areas are managed
for conservation (Ruth Island, Salt River Bay, and Buck Island National
Monument), the remaining populations occur within privately owned lands
currently threatened by development or areas already developed and
managed as tourism and residential projects. Based on information
reported by the University of the Virgin Islands' Conservation Data
Center (https://cdc.uvi.edu), at least three of the populations
(Protestant Cay, Gallows Bay, and Ha'penny Beach) lie within areas
identified by the DPNR as high-density land use areas, which have a
higher susceptibility to development in the near future. Furthermore,
Weiss (2010, pers. comm.) identified two proposed development projects
within suitable habitat for the species (C&R Robin, LLC and Seven Hills
Beach Resort and Casino). Based on the field assessment conducted by
Service biologists, the coastal areas that harbor suitable habitat for
the species are currently subject to urban and tourist development
(Monsegur and Vargas 2010, personal observation).
The population at Protestant Cay seems to be affected by the use of
the area as a deposit for garden debris from a hotel that occupies the
majority of this small island (Monsegur and Vargas 2010, personal
observation). Since Agave eggersiana relies on asexual reproduction,
the species depends on the bulbils becoming established. Covering the
bulbils with debris may result in subsequent mortality of the bulbils
and lack of natural recruitment, thus affecting the long-term survival
of this population. Moreover, individuals located on the edges of the
population are pruned as part of the gardens' maintenance. This
practice may result in mortality or mutilation of individuals since the
species is monopodial (single growth axis). The population at
Protestant Cay is also threatened by competition with exotic plant
species. Individuals seem to be stressed due to competition with
exotics as what little undeveloped habitat is left is rapidly being
colonized by nonnative species (see Factor E).
The individuals located at Gallows Bay are within an area currently
developed as a residential complex with the potential for future
expansion, which may affect these individuals (Monsegur and Vargas
2010, personal observation). In addition, this area does not contain
additional habitat to allow the current population to expand. Remaining
forested areas surrounding this location are characterized by the
abundance of exotic species. Areas that could be used by bulbils to
become established are occupied by the exotic plant Sansevieria
cilindrica, a species that tends to form a complete cover of the
understory (see Factor E).
The areas adjacent to Ha'penny Bay on the south coast of St. Croix
harbor two of the known natural populations of Agave eggersiana
(Ha'penny Beach and South Shore). According to personnel from the DPNR
(Valiulis 2010, pers. comm.) these areas are advertised by realtors as
areas for tourism and residential development and, as previously
mentioned, are planned for high-density development. Furthermore, the
areas along the south coast that have not been developed are used for
cattle or hay production, minimizing the recovery of native vegetation
and, therefore, the habitat for A. eggersiana (Monsegur and Vargas
2010, personal observation). The development of tourist and residential
projects in these coastal areas may result in the extirpation of some
populations, or at the least, will reduce the chances of the
populations to expand or to colonize other areas. This is exacerbated
by the low potential for natural recruitment due to the small number of
populations and individuals.
The population of Great Pond is located between the entrance road
of the East End Marine Park office and a private property currently for
sale. The population seems to be healthy based on the presence of
different size plants and evidence of recent flowering events. It seems
that there is suitable habitat for the species in the area; however,
the area near the population is mowed and the access road limits the
expansion of the population's range. Furthermore, the area adjacent to
this population is a private property for sale. The possible use of the
area for residential or tourist development may affect the population;
owners will likely manage their properties as landscapes, which could
lead to land clearing, additional mowing, and other maintenance of
gardens. This could also lead to the introduction of exotics. Moreover,
the abundance of grassland areas and the dominance of the exotic
Megathyrsus maximus (guinea grass) in the area make the population
Agave eggersiana susceptible to human-induced fires (addressed in
Factor E). These exotic grasses are typically adapted to fire
conditions.
Based on the above information, we consider the present or
threatened destruction, modification, or curtailment of the species
habitat or range as a moderate but imminent threat to wild populations
of Agave eggersiana. The threats of possible construction developments
and current management of habitat of the populations may further limit
species
[[Page 57724]]
propagation and expansion in the foreseeable future.
Factor B: Overutilization for Commercial, Recreational, Scientific, or
Educational Purposes
Agave eggersiana has been reported as a cultivar since it was
described as a species in 1913 (Trelease, 1913, p. 28); historically,
the majority of A. eggersiana found in St. Croix and St. Thomas were
from landscaped areas (Britton and Wilson 1923, p. 156; Plaskett 2003,
pers. comm.; Kojis and Boulon 1996, pers. comm.; Proctor and Acevedo-
Rodri[acute]guez 2005, p. 118; Acevedo-Rodri[acute]guez 2005, pers.
comm.). The species is currently distributed by the St. George
Botanical Garden for conservation and private landscaping purposes. A.
eggersiana is a commonly used ornamental species on the island, and
recent declines in the number of individuals at one population along
the coast of Ha'penny Bay are thought to be due to collection for
ornamental purposes (Dalmida-Smith 2010, pers. comm.; Valiulis 2010,
pers. comm.).
Based on the above, we consider the overutilization for commercial
and recreational purposes a moderate to low but imminent threat to wild
populations of the species. Although captively propagated Agave
eggersiana are available to residents for use in private gardens,
collection of wild individuals is a threat to the species, and we
expect it to continue to be a threat in the foreseeable future.
Factor C: Disease or Predation
The genus Agave is widely affected by the agave snout weevil
(Scyphophorus acupunctatus). This weevil has a wide distribution that
includes the Greater Antilles (Cuba, Jamaica and Hispaniola) (Vaurie
1971, p. 4). The larvae of this weevil feed on the starchy base of the
plant, increasing the risk of infestation by pathogens, such as a virus
or fungus, later resulting in the death of the plant (Vaurie 1971, p.
4). At this time, there is no information about the occurrence of the
agave snout weevil within the Puerto Rican Platform or the Lesser
Antilles where St. Croix is located. A small number of individuals of
A. eggersiana were observed with scarring along the borders of some
leaves (Monsegur and Vargas 2010, personal observation). It appears
that an insect or an arthropod larva may feed on the leaves; however,
the exact cause and the consequences of the scarring are unknown.
Nevertheless, this is important and it should be monitored as it might
be an indicator of a recently arrived pest to St Croix.
On Mona Island (Puerto Rico), feral pigs are known to uproot
juveniles and destroy the root system of Agave sisalana, to feed on the
root system or to use them as a water source (Saliva 1983, 1996,
personal observation). Since introduced pigs, donkeys, and goats have
been reported in St. Croix we cannot discard the possible predation of
A. eggersiana by these feral animals, particularly to young plants
within the populations. The absence of evidence of predation by these
species might be the result of the low number of populations of A.
eggersiana, their isolation, and the proximity of some of these
populations to human inhabited areas. However, at this time, there is
no evidence that donkeys, pigs, or goats constitute a specific threat
to any A. eggersiana populations.
Since the agave snout weevil has not been reported in St. Croix, we
do not consider disease as a threat to the species. Although there is
some evidence that insect or arthropod larvae may feed on the leaves of
Agave eggersiana, there is no evidence that this is negatively
impacting the species' ability to grow or reproduce. In addition, we
have no evidence of grazing on A. eggersiana by introduced donkeys,
pigs, or goats. Therefore, we do not find disease or predation to be a
current threat to the species.
Factor D: The Inadequacy of Existing Regulatory Mechanisms
The Territory of the U.S. Virgin Islands currently considers Agave
eggersiana to be endangered under the Virgin Islands Indigenous and
Endangered Species Act (V.I. Code, Title 12, Chapter 2), and has
amended an existing regulation (Bill No. 18-0403) to provide for
protection of endangered and threatened wildlife and plants by
prohibiting the take, injury, or possession of indigenous plants. Based
on the number of individuals currently used for private gardens and
current landscape practices in private areas, such as pruning and
mowing of populations, we believe that protection provisions under the
local regulation are not being appropriately enforced. Rothenberger et
al. (2008, p. 68) mentioned that the lack of management and enforcement
capacity continues to be a significant challenge for the USVI since
enforcement agencies are chronically understaffed and territorial
resource management offices experience significant staff turnover,
particularly during administration changes.
Based on the information above, we consider the inadequacy of
existing regulatory mechanisms as a current threat to the species due
to a lack of enforcement. Because at least three populations exist in
areas managed for conservation and public outreach, we consider this
threat to be moderate to low in magnitude but imminent. We do not
anticipate any regulatory or enforcement changes that would reduce this
threat in the foreseeable future.
Factor E: Other Natural or Manmade Factors Affecting the Continued
Existence of the Species
The islands of the Caribbean are frequently affected by hurricanes.
It has been suggested that hurricanes are responsible for shaping and
modifying the structure and composition of the vegetation in the
Caribbean (Van Bloem et al. 2003, p. 137; Van Bloem et al. 2005, p.
572; Van Bloem et al. 2006, p. 517). As an endemic species to the
island of St. Croix, Agave eggersiana would be expected to be well
adapted to tropical storms. However, the low number of individuals
found on the island and the reproductive biology of the species
(dependence on asexual reproduction and the plant dying after
flowering) increases the likelihood of stochastic events such as
hurricanes extirpating a population. We believe that landslides and
coastal erosion associated with hurricanes may affect the populations
located along the coastal areas of St. Croix (Ha'penny Beach, South
Shore, and Protestant Cay) due to their proximity to cliffs and the
shoreline.
Agave eggersiana may be further threatened by climate change, which
is predicted to increase the frequency and strength of tropical storms
and can cause severe droughts (Hopkinson et al. 2008, p. 260). The
cumulative effect of coastal erosion due to severe hurricanes plus the
habitat modification for urban and tourist development can further
diminish the availability of suitable habitat and, therefore, limit
population expansion and colonization of new areas. In addition, the
possibility of severe droughts may contribute to an increase in the
quantity and frequency of fires on the island. These cumulative factors
may reduce the number of individuals and further reduce populations.
Based on satellite images, there is evidence of human-induced fires
along the south coast of the island. The vegetation of the Caribbean is
not adapted to fires since this disturbance does not naturally occur on
these islands (Brandeis and Woodall 2008, p. 557; Santiago-
Garci[aacute] et al. 2008, p. 608); juvenile plants are especially
vulnerable to fire damage. This regime of human-induced fires could
modify the landscape by promoting exotic trees and
[[Page 57725]]
grasses, and by diminishing the seed bank of native species. For
example the exotic Megathyrsus maximus is well adapted to fires and
typically colonizes areas that were previously covered by native
vegetation. Furthermore, the presence of this species increases the
amount of fuel and, therefore, the intensity of the fire events. Due to
the abundance of grasses at Great Pond, this Agave eggersiana
population is particularly threatened by human-induced fires.
Moreover, the individuals of the populations of Protestant Cay,
Gallows Bay and Great Pond are surrounded by dense stands of different
species of Sansevieria, an herb native to Africa. This invasive species
seems to be occupying the ecological niche adjacent to the known
populations of Agave eggersiana. Plant invasion can affect the
environment at three levels; at the genetic level the number of
individuals of native species can be reduced below the minimum
necessary for persistence, at the species diversity level the number of
species present and their distribution can be reduced, and at the
ecosystem level the functioning of the ecosystem can be changed (Rippey
et al. 2002, p. 170). In this case, invasive species may constrain the
number of A. eggersiana reducing variability in the population.
Consequently, the loss of diversity of the species may eliminate A.
eggersiana in the area affecting other organisms (e.g., insects and
birds feeding on the flowers).
Based on the above information and due to the reduced number of
populations and individuals, we believe that the species is currently
threatened by natural or manmade factors such as hurricanes, fires, and
competition from exotic species. Climate change may exacerbate these
habitat threats by increasing the frequency of fires, droughts, and
hurricanes. We consider these threats to be moderate and imminent. We
do not anticipate any changes that would appreciably reduce this threat
in the foreseeable future.
Finding
As required by the Act, we conducted a review of the status of the
species and considered the five factors in assessing whether Agave
eggersiana is threatened or endangered throughout all or a significant
portion of its range. We examined the best scientific and commercial
information available regarding the past, present, and future threats
faced by the species. We reviewed the petition, information available
in our files, other available published and unpublished information,
consulted with species and habitat experts and other Federal and State
agencies, and conducted field work on the island of St. Croix.
This status review identified threats to the species attributable
to Factors A, B, D, and E. Of the currently known populations, only
three populations are located in areas managed for conservation and
public outreach (Ruth Island, Salt River Bay, and Buck Island National
Monument). The remaining populations, containing about 97 percent of
the currently known adult individuals, are located in areas either
threatened by development pressure, or are currently affected by
landscape practices and competition with exotic species, resulting in
detrimental effects to reproduction and recruitment (see Factors A and
E). Furthermore, the use of the Agave eggersiana as an ornamental
species is common on the island, and evidence suggests that wild
specimens are being collected due to the commercial interest in this
species (Factor B). Although the species is currently listed under
local regulations, lack of enforcement of local law does not provide
adequate protection to ameliorate threats to the species.
On the basis of the best scientific and commercial information
available and our analysis of the current and foreseeable threats to
the species and its habitat, we find that listing Agave eggersiana
(including wild and cultivated populations), is warranted. We will make
a determination on the status of the species as threatened or
endangered when we do a proposed listing determination. However, as
explained in more detail below, an immediate proposal of a regulation
implementing this action is precluded by higher priority listing
actions, and progress is being made to add or remove qualified species
from the Lists of Endangered and Threatened Wildlife and Plants.
We reviewed the available information to determine if the existing
and foreseeable threats render the species at risk of extinction now
such that issuing an emergency regulation temporarily listing the
species as per section 4(b)(7) of the Act is warranted. We determined
that issuing an emergency regulation temporarily listing the species is
not warranted for this species at this time since approximately 450
individuals are known to occur in 10 localities (Table 1). However, if
at any time we determine that issuing an emergency regulation
temporarily listing the species is necessary, we will initiate this
action at that time.
Listing Priority Number
The Service adopted guidelines on September 21, 1983 (48 FR 43098),
to establish a rational system for utilizing available resources for
the highest priority species when adding species to the Lists of
Endangered or Threatened Wildlife and Plants or reclassifying species
listed as threatened to endangered status. The system places greatest
importance on the immediacy and magnitude of threats, but also factors
in the level of taxonomic distinctiveness by assigning priority in
descending order to monotypic genera, full species, and subspecies (or
equivalently, distinct population segments of vertebrates).
We assigned Agave eggersiana an LPN of 8, based on our finding that
the species faces moderate to low magnitude threats from the present or
threatened destruction, modification, or curtailment of its habitat;
overutilization for commercial, recreational, scientific, or
educational purposes; the inadequacy of existing regulatory mechanisms;
and other natural or manmade Factors. One or more of the threats
discussed above are occurring, and we anticipate they will still occur
in the near future in each known population in St. Croix. These threats
are ongoing and in some cases considered irreversible.
Although the species faces threats, as described above, we believe
these threats to be of moderate to low magnitude; at least 450 adults
and 260 bulbils are known to occur in 10 populations with half showing
evidence of recruitment in the wild and 3 located in areas managed for
conservation and public outreach. Under the 1983 Guidelines, a
``species'' facing imminent moderate to low magnitude threats is
assigned an LPN of 7, 8, or 9 depending on its taxonomic status.
Because A. eggersiana is a species, but not a monotypic genus, we
assigned it an LPN of 8. While we conclude that listing the species is
warranted, an immediate proposal to list this species is precluded by
other higher priority listing actions, which we address below.
Preclusion and Expeditious Progress
Preclusion is a function of the listing priority of a species in
relation to the resources that are available and competing demands for
those resources. Thus, in any given fiscal year (FY), multiple factors
dictate whether it will be possible to undertake work on a proposed
listing regulation or whether promulgation of such a proposal is
warranted but precluded by higher-priority listing actions.
[[Page 57726]]
The resources available for listing actions are determined through
the annual Congressional appropriations process. The appropriation for
the Listing Program is available to support work involving the
following listing actions: proposed and final listing rules; 90-day and
12-month findings on petitions to add species to the Lists of
Endangered and Threatened Wildlife and Plants (Lists) or to change the
status of a species from threatened to endangered; annual
determinations on prior ``warranted but precluded'' petition findings
as required under section 4(b)(3)(C)(i) of the Act; critical habitat
petition findings; proposed and final rules designating critical
habitat; and litigation-related, administrative, and program-management
functions (including preparing and allocating budgets, responding to
Congressional and public inquiries, and conducting public outreach
regarding listing and critical habitat). The work involved in preparing
various listing documents can be extensive and may include, but is not
limited to: gathering and assessing the best scientific and commercial
data available and conducting analyses used as the basis for our
decisions; writing and publishing documents; and obtaining, reviewing,
and evaluating public comments and peer review comments on proposed
rules and incorporating relevant information into final rules. The
number of listing actions that we can undertake in a given year also is
influenced by the complexity of those listing actions; that is, more
complex actions generally are more costly. For example, during the past
several years, the cost (excluding publication costs) for preparing a
12-month finding, without a proposed rule, has ranged from
approximately $11,000 for one species with a restricted range and
involving a relatively uncomplicated analysis to $305,000 for another
species that is wide-ranging and involving a complex analysis.
We cannot spend more than is appropriated for the Listing Program
without violating the Anti-Deficiency Act (see 31 U.S.C. Sec.
1341(a)(1)(A)). In addition, in FY 1998 and for each fiscal year since
then, Congress has placed a statutory cap on funds that may be expended
for the Listing Program, equal to the amount expressly appropriated for
that purpose in that fiscal year. This cap was designed to prevent
funds appropriated for other functions under the Act (for example,
recovery funds for removing species from the Lists), or for other
Service programs, from being used for Listing Program actions (see
House Report 105-163, 105\th\ Congress, 1st Session, July 1, 1997).
Recognizing that designation of critical habitat for species
already listed would consume most of the overall Listing Program
appropriation, Congress also put a critical habitat subcap in place in
FY 2002 and has retained it each subsequent year to ensure that some
funds are available for other work in the Listing Program: ``The
critical habitat designation subcap will ensure that some funding is
available to address other listing activities'' (House Report No. 107 -
103, 107\th\ Congress, 1st Session, June 19, 2001). In FY 2002 and each
year until FY 2006, the Service has had to use virtually the entire
critical habitat subcap to address court-mandated designations of
critical habitat, and consequently none of the critical habitat subcap
funds have been available for other listing activities. In FY 2007, we
were able to use some of the critical habitat subcap funds to fund
proposed listing determinations for high-priority candidate species. In
FY 2009, while we were unable to use any of the critical habitat subcap
funds to fund proposed listing determinations, we did use some of this
money to fund the critical habitat portion of some proposed listing
determinations, so that the proposed listing determination and proposed
critical habitat designation could be combined into one rule, thereby
being more efficient in our work. In FY 2010, we are using some of the
critical habitat subcap funds to fund actions with statutory deadlines.
Thus, through the listing cap, the critical habitat subcap, and the
amount of funds needed to address court-mandated critical habitat
designations, Congress and the courts have in effect determined the
amount of money available for other listing activities. Therefore, the
funds in the listing cap, other than those needed to address court-
mandated critical habitat for already-listed species, set the limits on
our determinations of preclusion and expeditious progress.
Congress also recognized that the availability of resources was the
key element in deciding, when making a 12-month petition finding,
whether we would prepare and issue a listing proposal or instead make a
``warranted but precluded'' finding for a given species. The Conference
Report accompanying Public Law 97-304, which established the current
statutory deadlines and the warranted-but-precluded finding, states (in
a discussion on 90-day petition findings that by its own terms also
covers 12-month findings) that the deadlines were ``not intended to
allow the Secretary to delay commencing the rulemaking process for any
reason other than that the existence of pending or imminent proposals
to list species subject to a greater degree of threat would make
allocation of resources to such a petition [that is, for a lower-
ranking species] unwise.''
In FY 2010, expeditious progress is that amount of work that can be
achieved with $10,471,000, which is the amount of money that Congress
appropriated for the Listing Program (that is, the portion of the
Listing Program funding not related to critical habitat designations
for species that are already listed). However these funds are not
enough to fully fund all our court-ordered and statutory listing
actions in FY 2010, so we are using $1,114,417 of our critical habitat
subcap funds in order to work on all of our required petition findings
and listing determinations. This brings the total amount of funds we
have for listing action in FY 2010 to $11,585,417. Starting in FY 2010,
we are also using our funds to work on listing actions for foreign
species since that work was transferred from the Division of Scientific
Authority, International Affairs Program to the Endangered Species
Program. Our process is to make our determinations of preclusion on a
nationwide basis to ensure that the species most in need of listing
will be addressed first and also because we allocate our listing budget
on a nationwide basis. The $11,585,417 is being used to fund work in
the following categories: compliance with court orders and court-
approved settlement agreements requiring that petition findings or
listing determinations be completed by a specific date; section 4 (of
the Act) listing actions with absolute statutory deadlines; essential
litigation-related, administrative, and listing program-management
functions; and high-priority listing actions for some of our candidate
species. The allocations for each specific listing action are
identified in the Service's FY 2010 Allocation Table (part of our
administrative record).
In FY 2007, we had more than 120 species with an LPN of 2, based on
our September 21, 1983, guidance for assigning an LPN for each
candidate species (48 FR 43098). Using this guidance, we assign each
candidate an LPN of 1 to 12, depending on the magnitude of threats
(high vs. moderate to low), immediacy of threats (imminent or
nonimminent), and taxonomic status of the species (in order of
priority: monotypic genus (a species that is the sole member of a
genus); species; or part
[[Page 57727]]
of a species (subspecies, distinct population segment, or significant
portion of the range)). The lower the listing priority number, the
higher the listing priority (that is, a species with an LPN of 1 would
have the highest listing priority).
To be more efficient in our listing process, as we work on proposed
rules for these species in the next several years, we are preparing
multi-species proposals when appropriate, and these may include species
with lower priority if they overlap geographically or have the same
threats as a species with an LPN of 2. In addition, available staff
resources are also a factor in determining which high-priority species
are provided with funding. Finally, proposed rules for reclassification
of threatened species to endangered are lower priority, since as listed
species, they are already afforded the protection of the Act and
implementing regulations.
Given the above-mentioned funding constraints, the Service's
priority is to work on: (1) listing determinations for listing actions
with absolute statutory, court-ordered, or court-approved deadlines,
and final listing determinations for those species that have been
proposed for listing; and (2) candidate species and reclassifications
of other higher priority threatened species (i.e., species with LPN of
1). This work includes all the actions listed in the tables below under
expeditious progress.
As explained above, a determination that listing is warranted but
precluded must also demonstrate that expeditious progress is being made
to add or remove qualified species to and from the Lists of Endangered
and Threatened Wildlife and Plants. (Although we do not discuss it in
detail here, we are also making expeditious progress in removing
species from the list under the Recovery program, which is funded by a
separate line item in the budget of the Endangered Species Program. As
explained above in our description of the statutory cap on Listing
Program funds, the Recovery Program funds and actions supported by them
cannot be considered in determining expeditious progress made in the
Listing Program.) As with our ``precluded'' finding, expeditious
progress in adding qualified species to the Lists is a function of the
resources available and the competing demands for those funds. Given
that limitation, we find that we made progress in FY 2009 in the
Listing Program and will continue to make progress in FY 2010. This
progress included preparing and publishing the following
determinations:
FY 2010 Completed Listing Actions
----------------------------------------------------------------------------------------------------------------
Publication Date Title Actions FR Pages
----------------------------------------------------------------------------------------------------------------
10/08/2009 Listing Lepidium papilliferum Final Listing 74 FR 52013-52064
(Slickspot Peppergrass) as a Threatened..........
Threatened Species
Throughout Its Range
----------------------------------------------------------------------------------------------------------------
10/27/2009 90-day Finding on a Petition Notice of 90-day 74 FR 55177-55180
To List the American Dipper Petition Finding,...
in the Black Hills of South Not substantial.....
Dakota as Threatened or
Endangered
----------------------------------------------------------------------------------------------------------------
10/28/2009 Status Review of Arctic Notice of Intent to 74 FR 55524-55525
Grayling (Thymallus Conduct Status......
arcticus) in the Upper Review..............
Missouri River System
----------------------------------------------------------------------------------------------------------------
11/03/2009 Listing the British Columbia Proposed Listing 74 FR 56757-56770
Distinct Population Segment Threatened..........
of the Queen Charlotte
Goshawk Under the Endangered
Species Act
----------------------------------------------------------------------------------------------------------------
11/03/2009 Listing the Salmon-Crested Proposed Listing 74 FR 56770-56791
Cockatoo as Threatened Threatened
Throughout Its Range with
Special Rule
----------------------------------------------------------------------------------------------------------------
11/23/2009 Status Review of Gunnison Notice of Intent to 74 FR 61100-61102
sage-grouse (Centrocercus Conduct Status
minimus) Review..............
----------------------------------------------------------------------------------------------------------------
12/03/2009 12-Month Finding on a Notice of 12-month 74 FR 63343-63366
Petition to List the Black- petition finding,
tailed Prairie Dog as Not warranted
Threatened or Endangered
----------------------------------------------------------------------------------------------------------------
12/03/2009 90-Day Finding on a Petition Notice of 90-day 74 FR 63337-63343
to List Sprague's Pipit as Petition Finding,...
Threatened or Endangered..... Substantial.........
----------------------------------------------------------------------------------------------------------------
12/15/2009 90-Day Finding on Petitions Notice of 90-day 74 FR 66260-66271
To List Nine Species of Petition Finding,...
Mussels From Texas as Substantial.........
Threatened or Endangered
With Critical Habitat
----------------------------------------------------------------------------------------------------------------
12/16/2009 Partial 90-Day Finding on a Notice of 90-day 74 FR 66865-66905
Petition to List 475 Species Petition Finding,...
in the Southwestern United Not substantial and.
States as Threatened or Substantial.........
Endangered With Critical
Habitat
----------------------------------------------------------------------------------------------------------------
12/17/2009 12-month Finding on a Notice of 12-month 74 FR 66937-66950
Petition To Change the Final petition finding,
Listing of the Distinct Warranted but
Population Segment of the precluded...........
Canada Lynx To Include New
Mexico
----------------------------------------------------------------------------------------------------------------
1/05/2010 Listing Foreign Bird Species Proposed Listing 75 FR 605-649
in Peru and Bolivia as Endangered..........
Endangered Throughout Their
Range
----------------------------------------------------------------------------------------------------------------
[[Page 57728]]
1/05/2010 Listing Six Foreign Birds as Proposed Listing 75 FR 286-310
Endangered Throughout Their Endangered..........
Range
----------------------------------------------------------------------------------------------------------------
1/05/2010 Withdrawal of Proposed Rule Proposed rule, 75 FR 310-316
to List Cook's Petrel withdrawal..........
----------------------------------------------------------------------------------------------------------------
1/05/2010 Final Rule to List the Final Listing 75 FR 235-250
Galapagos Petrel and Threatened..........
Heinroth's Shearwater as
Threatened Throughout Their
Ranges
----------------------------------------------------------------------------------------------------------------
1/20/2010 Initiation of Status Review Notice of Intent to 75 FR 3190-3191
for Agave eggersiana and Conduct Status
Solanum conocarpum Review..............
----------------------------------------------------------------------------------------------------------------
2/09/2010 12-month Finding on a Notice of 12-month 75 FR 6437-6471
Petition to List the American petition finding,
Pika as Threatened or Not warranted
Endangered.
----------------------------------------------------------------------------------------------------------------
2/25/2010 12-Month Finding on a Notice of 12-month 75 FR 8601-8621
Petition To List the Sonoran petition finding,
Desert Not warranted
Population of the Bald Eagle
as a Threatened or
Endangered.
Distinct Population Segment..
----------------------------------------------------------------------------------------------------------------
2/25/2010 Withdrawal of Proposed Rule Withdrawal of 75 FR 8621-8644
To List the Southwestern Proposed Rule to....
Washington/Columbia River List................
Distinct Population Segment
of Coastal Cutthroat Trout
(Oncorhynchus clarki clarki)
as.
Threatened...................
----------------------------------------------------------------------------------------------------------------
3/18/2010 90-Day Finding on a Petition Notice of 90-day 75 FR 13068-13071
to List the Berry Cave Petition Finding,...
Salamander as Endangered Substantial.........
----------------------------------------------------------------------------------------------------------------
3/23/2010 90-Day Finding on a Petition Notice of 90-day 75 FR 13717-13720
to List the Southern Petition Finding,...
Hickorynut Not substantial.....
Mussel (Obovaria jacksoniana)
as Endangered or Threatened.
----------------------------------------------------------------------------------------------------------------
3/23/2010 90-Day Finding on a Petition Notice of 90-day 75 FR 13720-13726
to List the Striped Newt as Petition Finding,...
Threatened................... Substantial.........
----------------------------------------------------------------------------------------------------------------
3/23/2010 12-Month Findings for Notice of 12-month 75 FR 13910-14014
Petitions to List the petition finding,
Greater Sage-Grouse Warranted but.......
(Centrocercus urophasianus) precluded...........
as Threatened or Endangered..
----------------------------------------------------------------------------------------------------------------
3/31/2010 12-Month Finding on a Notice of 12-month 75 FR 16050-16065
Petition to List the Tucson petition finding,
Shovel-Nosed Snake Warranted but.......
(Chionactis occipitalis precluded...........