Endangered and Threatened Wildlife and Plants; 90-Day Finding on a Petition To List the Smooth-Billed Ani as Threatened or Endangered, 23265-23271 [2011-9975]
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Federal Register / Vol. 76, No. 80 / Tuesday, April 26, 2011 / Proposed Rules
jlentini on DSKJ8SOYB1PROD with PROPOSALS
al. 2005, p. 217). Disturbances such as
wildfire and insect outbreaks are
increasing and are likely to intensify
with drier soils and a longer growing
season (Field et al. 2007, p. 619). The
mountain pine beetle has expanded its
range into areas previously too cold to
support it (Field et al. 2007, p. 623;
Saunders et al. 2008, pp. 21, 23). The
USFS predicts that in Colorado and
southern Wyoming, mountain pine
beetles will likely kill the majority of
mature lodgepole pine forests within the
next 3 to 5 years (Saunders et al. 2008,
pp. 21 and 23).
Aquatic insects may respond to
elevated temperatures in the following
ways: (1) Behaviorally, by emigrating
from, or changing distribution within,
stressed regions; or (2) physiologically,
by adjusting the duration and extent of
growth and development in immature
stages, and ultimate size, condition, and
fecundity as adults (Williams and
Feltmate 1992, p. 285). Impacts from
global warming will vary greatly at the
species level (Williams and Feltmate
1992, p. 287). The Arapahoe snowfly
will likely be affected by warmer
streamflows and by continuing
outbreaks of mountain pine beetle.
However, we cannot predict the extent
to which the species will be able to
adjust behaviorally or physiologically to
these changes. We will assess this factor
more thoroughly during our status
review for the species.
In summary, we find that the
information provided in the petition, as
well as other information readily
available in our files, presents
substantial scientific or commercial
information indicating that the
petitioned action may be warranted due
to other natural or manmade factors
affecting its continued existence such as
the apparent small population size of
the Arapahoe snowfly, especially given
the stressors it faces from recreation,
grazing, and certain forest management
practices. The species also will likely be
affected by climate change; however, we
cannot currently predict the extent to
which it will be able to adjust to these
changes.
Finding
On the basis of our determination
under section 4(b)(3)(A) of the Act, we
have determined that the petition
presents substantial scientific or
commercial information indicating that
listing the Arapahoe snowfly throughout
its entire range may be warranted. This
finding is based on information
provided under factors A and E. The
information provided in the petition
under factors B, C, and D is not
substantial.
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We are not aware of any information
regarding impacts from factors A and E
that specifically pertains to the
Arapahoe snowfly. However, there is
adequate information documenting that
recreation, grazing, carbaryl spraying,
and road usage are ongoing in Elkhorn
Creek and that recreation is occurring in
Young Gulch. There also is adequate
information documenting the likely
adverse effects of these activities on
stoneflies. Consequently, we have
concluded that since the Arapahoe
snowfly is a species of stonefly, it is
likely being adversely affected by these
activities, particularly in view of its very
narrow known range and rarity within
that range. We will assess all of these
factors more thoroughly during our
status review for the species.
Because we have found that the
petition presents substantial
information indicating that listing the
Arapahoe snowfly may be warranted,
we are initiating a status review to
determine whether listing the Arapahoe
snowfly under the Act is warranted.
The ‘‘substantial information’’
standard for a 90-day finding differs
from the Act’s ‘‘best scientific and
commercial data’’ standard that applies
to a status review to determine whether
a petitioned action is warranted. A 90day finding does not constitute a status
review under the Act. In a 12-month
finding, we will determine whether a
petitioned action is warranted after we
have completed a thorough status
review of the species, which is
conducted following a substantial 90day finding. Because the Act’s standards
for 90-day and 12-month findings are
different, as described above, a
substantial 90-day finding does not
necessarily mean that the 12-month
finding will result in a warranted
finding.
References Cited
A complete list of references cited is
available on the Internet at https://
www.regulations.gov or upon request
from the Colorado Field Office (see FOR
FURTHER INFORMATION CONTACT).
Author
The primary authors of this notice are
staff members of the Regional Office and
the Colorado Field Office (see
ADDRESSES).
Authority: The authority for this action is
the Endangered Species Act of 1973, as
amended (16 U.S.C. 1531 et seq.).
Dated: April 13, 2011.
Rowan Gould,
Director, U.S. Fish and Wildlife Service.
[FR Doc. 2011–9973 Filed 4–25–11; 8:45 am]
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DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[Docket No. FWS–R4–ES–2011–0007; MO
92210–0–0008]
Endangered and Threatened Wildlife
and Plants; 90-Day Finding on a
Petition To List the Smooth-Billed Ani
as Threatened or Endangered
Fish and Wildlife Service,
Interior.
ACTION: Notice of 90-day petition
finding.
AGENCY:
We, the U.S. Fish and
Wildlife Service, announce a 90-day
finding on a petition to list the smoothbilled ani (Crotophaga ani) as
threatened or endangered under the
Endangered Species Act of 1973, as
amended (Act). Based on our review, we
find that the petition does not present
substantial information indicating that
listing the species may be warranted.
Therefore, we are not initiating a status
review in response to this petition.
However, we ask the public to submit to
us any new information that becomes
available concerning the status of, or
threats to, the smooth-billed ani or its
habitat at any time.
DATES: The finding announced in this
document was made on April 26, 2011.
ADDRESSES: This finding is available on
the Internet at https://
www.regulations.gov at Docket Number
FWS–R4–ES–2011–0007. 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, South Florida
Ecological Services Office, 1339 20th
Street, Vero Beach, Florida 32960–3559.
Please submit any new information,
materials, comments, or questions
concerning this finding to the above
address.
SUMMARY:
FOR FURTHER INFORMATION CONTACT:
Spencer Simon, Assistant Field
Supervisor, of the South Florida
Ecological Services Office (see
ADDRESSES) by telephone 772–562–
3909, or by facsimile to 772–562–4288.
If you use a telecommunications device
for the deaf (TDD), please call the
Federal Information Relay Service
(FIRS) at 800–877–8339.
SUPPLEMENTARY INFORMATION:
Background
Section 4(b)(3)(A) of the Act (16
U.S.C. 1531 et seq.) requires that we
make a finding on whether a petition to
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list, delist, or reclassify a species
presents substantial scientific or
commercial information indicating that
the petitioned action may be warranted.
We are to base this finding on
information provided in the petition,
supporting information submitted with
the petition, and information otherwise
available in our files. To the maximum
extent practicable, we are to make this
finding within 90 days of our receipt of
the petition and publish our notice of
the finding promptly in the Federal
Register.
Our standard for substantial scientific
or commercial information within the
Code of Federal Regulations (CFR) with
regard to a 90-day petition finding is
‘‘that amount of information that would
lead a reasonable person to believe that
the measure proposed in the petition
may be warranted’’ (50 CFR 424.14(b)).
If we find that substantial scientific or
commercial information was presented,
we are required to promptly conduct a
species status review, which we
subsequently summarize in our 12month finding.
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Petition History
On April 5, 2005, we received a
petition, dated March 23, 2005, from
Robert Showler of Homestead, Florida,
requesting that the smooth-billed ani
(Crotophaga ani), a bird, be listed as
endangered under the Act. The petition
clearly identified itself as such and
included the requisite identification
information for the petitioner(s), as
required by 50 CFR 424.14(a). In an
April 29, 2005, letter to the petitioner,
we responded that we received the
petition for the smooth-billed ani, and
that because of inadequate funding for
listing-related actions pursuant to court
orders and judicially approved
settlement agreements, we would not be
able to address the petition at that time.
We also noted that the species had been
included on the list of birds of
conservation concern in peninsular
Florida in 2002 and that we had begun
to compile information on this and
other species of conservation concern in
peninsular Florida. This finding
addresses the petition.
Species Information
The smooth-billed ani (Crotophaga
ani) is a member of the Family
Cuculidae (cuckoo family). We concur
with the petition’s taxonomic
characterization of the smooth-billed ani
(Crotophaga ani) as a species. This
species is a resident in parts of Florida,
the Caribbean, Mexico, and Central and
South America (Stevenson and
Anderson 1994, p. 355; Quinn and
Startek-Foote 2000, section 3, p. 1). The
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smooth-billed ani is a medium-sized
cuculid, with a length of 12–14 inches
(30–36 centimeters) and a mass of
approximately 3.5 ounces (100 grams)
(Ridgway 1916 and Loflin 1983 as cited
in Quinn and Startek-Foote 2000,
section 2, p. 1). Males tend to be slightly
larger than females (Quinn and StartekFoote 2000, section 2, p. 1). This species
is distinguished by: all-black plumage,
glossed with greenish or violet
iridescence in parts; a long tail
(approximately 6.8 in (17.2 cm)); a large,
arched, and laterally compressed bill,
usually showing a raised hump on the
basal half of the upper mandible; and a
distinctive call, including a whining
‘‘ah-nee,’’ which is usually delivered 1–
4 times, along with other vocalizations
(Quinn and Startek-Foote 2000, section
1, p. 1; section 2, p. 1; section 8, p. 1).
Immature birds resemble adults, but
their plumage contains a mixture of dull
and glossy blackish feathers, and the bill
is slightly shallower (Quinn and StartekFoote 2000, section 2, p. 1). Juveniles
are also similar in appearance to adults,
but with plumage that is entirely dull
blackish in color with little or no gloss,
and a smaller bill without a raised
hump (Quinn and Startek-Foote 2000,
section 2, p. 1).
The smooth-billed ani occurs over a
considerable global geographic range. It
is considered a resident from central
Florida south through the Caribbean,
and south into Central and South
America through Ecuador and northern
Argentina, except in the Andes
(Stevenson and Anderson 1994, p. 355;
Quinn and Startek-Foote 2000, section
3, p. 1). The species is generally
nonmigratory; however, some local
movement occurs during the dry season,
when many groups leave their territories
and gather in large flocks with
neighboring groups (Loflin 1983 as cited
in Quinn and Startek-Foote 2000,
section 5, p. 1). Records in the Dry
Tortugas suggest some movement
between the Caribbean and Florida
(Robertson and Woolfenden 1992 as
cited in Mlodinow and Karlson 1999, p.
241). This species may regularly
disperse from the Bahamas and Cuba to
Florida (Mlodinow and Karlson 1999, p.
242). The smooth-billed ani has been
described as a casual occurrence north
to North Carolina and west to Louisiana
(Stevenson and Anderson 1994, p. 355).
Vagrant records elsewhere in the United
States are scarce; few acceptable records
outside of Florida exist (e.g., New Jersey
or Pennsylvania, North Carolina, South
Carolina, and Georgia) (Mlodinow and
Karlson 1999, pp. 241–242).
Throughout its range, and year round,
the smooth-billed ani occupies savanna,
disturbed and human-altered rural and
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suburban areas, open areas with brush
or scrub, plantations, gardens,
farmlands, and forest clearings (Quinn
and Startek-Foote 2000, section 6, p. 1).
Preferred habitat is considered to be
open grassland (Blanchard 2000, p. 5).
In Puerto Rico, Guyana, Cuba, Jamaica,
´
Colombia, and the Galapagos Islands,
this species uses cow pastures and
adjacent lands (Quinn and Startek-Foote
2000, section 6, p. 1). In south Florida,
density was positively correlated with
amount of grazing lands and human
habitation (Loflin 1983 as cited in
Quinn and Startek-Foote 2000, section
6, p. 1). In general, this species typically
occupies lowlands, often near the coast,
preferring a source of water (e.g., marsh,
pond, river) and avoiding dense forest
(Quinn and Startek-Foote 2000, section
6, p. 1). In a study area in south Florida,
the smooth-billed ani was found to
occupy discontinuous patches of habitat
(e.g., parks, nurseries, small
undeveloped plots of land) and avoid
tall grasses of the Everglades (Loflin
1983 as cited in Quinn and StartekFoote 2000, section 6, p. 1).
Additionally, the species has been
found within and near impoundments
within the Loxahatchee National
Wildlife Refuge (NWR) (Service 1997, p.
48; 1998, p. 50; 1999a, p. 65; 2003a, pp.
113–114) and on various outer islands
within the Florida Keys NWR Complex
(Service 1992, p. 85; 1999b, p. 60; 2001,
p. 69; 2003b, p. 84).
This species feeds primarily on
insects and small vertebrates, especially
when these forage items are abundant
during the rainy season; fruit is an
important component of the diet during
the dry season (Quinn and Startek-Foote
2000, section 1, p. 1 and section 7, pp.
1–2; Blanchard 2000, p. 5). Fields of
grass are typically used for foraging;
more densely vegetated stream edges
may be used for nesting and roosting
(Quinn and Startek-Foote 2000, section
6, p. 1; Blanchard 2000, p. 5). The
smooth-billed ani is a highly social bird
that nests, roosts, feeds, and travels in
pairs or in communal groups (Quinn
and Startek-Foote 2000, section 9, p. 3;
Blanchard 2000, pp. 5–6). This species
uses a communal breeding system in
which a number of females lay eggs and
incubate in the same nest; late-laying
females bury the eggs of early-laying
females with twigs and leaves, which
can create a number of layers, but only
the top layer of eggs eventually hatches
(Quinn and Startek-Foote 2000, section
1, p. 1; Blanchard 2000, pp. 1–101).
Blanchard (2000, p. 30) found evidence
for monogamy, polygamy (extra-pair
fertilizations), and brood parasitism
(egg-laying in the nests of other birds) in
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both single-pair and group nests in a
study of the species’ communal
breeding system in Puerto Rico.
Observed nesting groups of smoothbilled anis ranged from a single pair to
12 adults and nests containing more
than 30 eggs (Blanchard 2000, p. 11).
Female-female competition at the nest
may result in the destruction of other
females’ eggs through egg burial under
nesting material (Blanchard 2000, p. 11).
The smooth-billed ani has a large
global population, estimated in 2004 to
be 20,000,000 individuals, with less
than or equal to 1 percent occurring in
the United States (Rich et al. 2004, p.
70). Global long-term trend data did not
exist at that time (Rich et al. 2004, p.
70). In general, little information on
global population size or trends was
available in Service files at the time the
petition was received. Available
information suggested that the smoothbilled ani’s conservation status was ‘‘not
threatened’’ (Quinn and Startek-Foote
2000, section 12, p. 1). The species was
not recognized as a National Audubon
Society Watch List Species or
Stewardship Species (Rich et al. 2004,
p. 70). The Audubon Watch List
categorizes species on the list if they are
declining rapidly and/or have very
small populations or limited ranges and
face major conservation threats (e.g.,
typically species of global conservation
concern) or if the species are either
declining or rare (e.g., typically species
of national conservation concern).
The smooth-billed ani is an
uncommon-to-rare resident of southern
Florida (Mlodinow and Karlson 1999, p.
241). Prior to the 1930s, few records
existed in Florida, suggesting that the
species was rare or poorly known
(Quinn and Startek-Foote 2000, section
3, p. 2). Sprunt (1939, pp. 335–336)
documented the first record of breeding
in Florida in 1938. By the late 1930s, the
species was considered established in
the Lake Okeechobee area, and
subsequently breeding was recorded
elsewhere in south Florida (Quinn and
Startek-Foote 2000, section 3, p. 2). The
species’ status in Florida remained
relatively unchanged until the 1960s,
when increasing numbers were recorded
in central and north Florida (Quinn and
Startek-Foote 2000, section 3, p. 2).
Based upon National Audubon Society
Christmas Bird Counts, the number
observed per party hour (p-hr) (average
number of counts per party per hour
spent censusing) tripled by 1962–63,
reaching 0.17 per p-hr in West Palm
Beach and 2.41 per p-hr in Fort
Lauderdale (Mlodinow and Karlson
1999, p. 241). In the 1960s the species
was fairly common to common from the
Everglades north to Brevard County on
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the east coast and Lee County on the
west coast (Mlodinow and Karlson
1999, p. 241). By 1968–69, the number
observed reached 1.51 per p-hr in West
Palm Beach and 4.20 per p-hr in Fort
Lauderdale (Mlodinow and Karlson
1999, p. 241).
Numbers appeared to have peaked in
Florida during the period 1968–1976,
when the species was recorded north to
Jacksonville Beach (Duval County) in
the east and St. Petersburg
(Hillsborough County) in the west
(Mlodinow and Karlson 1999, p. 241;
Quinn and Startek-Foote 2000, section
3, p. 2). At that time, numbers observed
were typically in the 3.0–4.0 per p-hr
range in Fort Lauderdale, while Fort
Pierce reached 1.87 per p-hr and Sanibel
Island/Captiva Island reached 0.41 per
p-hr (Mlodinow and Karlson 1999, p.
241). By winter 1977–1978, numbers
had declined sharply, returning to mid1960s levels (Mlodinow and Karlson
1999, p. 241). This decline continued,
and by 1988–1989, total numbers were
comparable to those reported in the
1950s (Mlodinow and Karlson 1999, p.
241). The decline continued in Florida
into the 1990s, and by 1998, the smoothbilled ani was found locally from the
Florida Keys north to West Palm Beach
on the east coast, and north to Collier
County on the west coast (Mlodinow
and Karlson 1999, pp. 241–242).
Mlodinow and Karlson (1999, p. 242)
suggested that the status of the smoothbilled ani in Florida in 1998 may be the
norm rather than an aberration.
Available information in Service files
suggests that the species uses
Loxahatchee NWR (Service, annual
narrative reports from 1996 to 2005) and
the Florida Keys NWR Complex
(Service, annual narrative reports from
1939 to 2003). According to a notation
in the 2000 annual narrative report from
Loxahatchee NWR, local long-time
birders have indicated that the numbers
of smooth-billed anis in south Florida
and on the Refuge have declined
significantly and that annual Christmas
Bird Counts are showing the same trend
(Service 2000, p. 110).
The reasons for expansion and
contraction of the species’ range in
Florida are not known. Expansion may
have been facilitated by residential
development, which resulted in
anthropogenic habitat changes that
initially favored this species (Mlodinow
and Karlson 1999, p. 242). However,
continued residential and agricultural
development, which reduced suitable
habitat, and exceptionally cold winters
during the 1970s may have contributed
to subsequent declines (Stevenson and
Anderson 1994, p. 357; Mlodinow and
Karlson 1999, p. 242). Overall, the
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reasons for the decline in south Florida
are not clear (Mlodinow and Karlson
1999, p. 242; National Audubon Society
2001, p. 335).
The smooth-billed ani was one of 668
taxa evaluated in an effort to help
prioritize vertebrate conservation efforts
in Florida (Millsap et al. 1990, pp. 3–
57). The evaluation system ranked taxa
(species and subspecies) according to
biological vulnerability, extent of
current knowledge of population status,
and management needs (Millsap et al.
1990, pp. 3–57). During this ranking
process, the smooth-billed ani was not
considered to be an imperiled taxon in
Florida as indicated from its biological
score, which was based upon facets of
its distribution, abundance, and life
history (Millsap et al. 1990, pp. 28–29).
Information available in Service files
at the time the petition was received
indicated that, in 2002, the Service’s
Division of Migratory Bird Management
included the smooth-billed ani as a bird
of conservation concern in peninsular
Florida in its report, entitled ‘‘Birds of
Conservation Concern 2002’’ (Service
2002, p. 68). The purpose of the report
was to identify migratory and
nonmigratory birds of the United States
and its territories that are of
conservation concern to encourage
coordinated and proactive conservation
actions among Federal, State, and
private partners (Service 2002, p. 3).
The overall goal of that report was to
accurately identify the migratory and
nonmigratory bird species (beyond
those already designated as federally
threatened or endangered) that
represented the Service’s highest
conservation priorities and draw
attention to species in need of
conservation action (Service 2002, p. 3).
The geographic scope of this endeavor
comprised the United States in its
entirety, including island ‘‘territories’’ in
the Pacific and Caribbean (Service 2002,
p. 1). Although the smooth-billed ani
was identified as one of 78 birds of
conservation concern in the Southeast,
only the U.S. mainland portion of the
Region was identified as of concern;
Puerto Rico and the U.S. Virgin Islands
were not identified as of concern
(Service 2002, p. 68). In addition, the
report does not include foreign
countries.
Evaluation of Information for This
Finding
Section 4 of the Act (16 U.S.C. 1533)
and its implementing regulations at 50
CFR part 424 set forth the procedures
for adding a species to, or removing a
species from, the Federal Lists of
Endangered and Threatened Wildlife
and Plants. A species may be
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determined to be an endangered or
threatened species due to one or more
of the five factors described in section
4(a)(1) of the Act:
(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 considering what factors might
constitute threats, we must look beyond
the mere exposure of the species to the
factor to determine whether the species
responds to the factor in a way that
causes actual impacts to the species. If
there is exposure to a factor, but no
response, or only a positive response,
that factor is not a threat. If there is
exposure and the species responds
negatively, the factor may be a threat
and we then attempt to determine how
significant a threat it is. If the threat is
significant, it may drive or contribute to
the risk of extinction of the species such
that the species may warrant listing as
threatened or endangered as those terms
are defined by the Act. This does not
necessarily require empirical proof of a
threat. The combination of exposure and
some corroborating evidence of how the
species is likely impacted could suffice.
The mere identification of factors that
could impact a species negatively may
not be sufficient to compel a finding
that listing may be warranted. The
information shall contain evidence
sufficient to suggest that these factors
may be operative threats that act on the
species to the point that the species may
meet the definition of threatened or
endangered under the Act.
In making this 90-day finding, we
evaluated whether information
regarding the threats to the smoothbilled ani, as presented in the petition
and other information available in our
files, is substantial, thereby indicating
that the petitioned action may be
warranted. Our evaluation of this
information is presented below.
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A. The Present or Threatened
Destruction, Modification, or
Curtailment of Its Habitat or Range
Information Provided in the Petition
The petition acknowledges that the
smooth-billed ani’s historic range in the
United States has largely been restricted
to southern Florida (Bent 1940; Terres
1980, p. 146) and that the species is
considered common in many parts of its
range throughout the Caribbean,
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including the Bahamas. The petition
states that numerous records in the Dry
Tortugas during the last 150 years
indicate that the species is capable of
traveling from Cuba to Florida (Birds of
North America Online). The petition
indicates that the species was reported
in low numbers in Florida during the
1800s and early 1900s (Sprunt 1932;
Bent 1940), with the first report of
breeding in Florida in 1938 (Sprunt
1932; Terres 1980, p. 146). It also cites
records from Louisiana and North
Carolina dating back to the early 1800s
(Bent 1940). The petition suggests that
the species seems to have experienced
an increase in population from the late
1950s through the early 1970s, and then
a rapid decline from the 1970s to 2005.
The petition claims that smooth-billed
anis are extremely rare everywhere in
the United States, noting data from
various National Audubon Society
Christmas Bird Counts.
The petition indicates that the species
generally prefers ‘‘open’’ habitats, such
as weedy and shrubby fields, pastures,
farmland, and occasionally residential
areas. Based upon a variety of
unspecified sources, the petition states
that the species is not commonly found
in heavily forested or extensive
marshes.
The petition states that rapid human
population growth and associated
development throughout peninsular
Florida, much of it occurring within the
species’ preferred habitat and historic
range, may be a potential contributor to
the decline of the smooth-billed ani.
The petition provides the following
statement: ‘‘Apparently [the ani is]
declining as southern Florida continues
to develop, and the brushland shrub/
scrub habitat is lost (Alsop 2002).’’ No
additional information or citations
relating to habitat loss as a threat are
given in the petition.
Evaluation of Information Provided in
the Petition and Available in Service
Files
The smooth-billed ani appears to have
declined from previous high levels in
Florida (Stevenson and Anderson 1994,
pp. 356–357; Mlodinow and Karlson
1999, p. 242; National Audubon Society
2005, pp. 1–3). However, it has been
suggested that this species’ current
status in Florida may be the norm rather
than an aberration (Mlodinow and
Karlson 1999, p. 242). It was not until
1938 that the species was established
and breeding in Florida (Sprunt 1939,
pp. 335–336; Stevenson and Anderson
1994, p. 355). One hypothesis suggests
that prior to the World War I era, south
Florida had little suitable smooth-billed
ani habitat, since it was largely a
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wetland surrounded by an inner zone of
pine forests and outer zones of
mangroves and sandy beaches
(Mlodinow and Karlson 1999, p. 242).
Substantial anthropogenic changes
beginning in the 1920s, consisting of
agricultural development and low-level
residential development, may have
created enough suitable habitat for
dispersing anis to successfully colonize
south Florida in the 1930s (Mlodinow
and Karlson 1999, p. 242). Over time,
residential development increased and
more intensive agricultural practices
and other factors may have reduced
suitable habitat and dispersal habitat,
causing decreased reproductive success
and lower recruitment (Mlodinow and
Karlson 1999, p. 242). Alsop (2002, p.
212) noted that the smooth-billed ani is
apparently declining in south Florida as
the area continues to develop and
brushland shrub/scrub habitat is lost.
Information in our files supports the
statement in the petition that human
population growth and associated landuse changes are occurring in peninsular
Florida, and that additional growth is
expected in the future. In the 50 years
prior to 1994, more than 8 million acres
[(3.24 million hectares (ha)] of forest
and wetland habitats (roughly 24
percent of the State) were cleared to
accommodate an expanding human
population (Cox et al. 1994, p. i).
Statewide, between 1936 and 1987,
cropland and rangeland increased by
4.25 million acres (1.72 million ha), or
30 percent; urban areas increased by
3.95 million acres (1.60 million ha), or
538 percent; herbaceous wetlands
declined by 3.88 million acres (1.57
million ha), or 56 percent; and forests
declined by 4.30 million acres (1.74
million ha), or 21 percent (Service
1999c, p. 4–128).
Although some anthropogenic habitat
changes may initially favor this species,
areas where the smooth-billed ani can
be locally found in Florida, from the
Keys north to West Palm Beach on the
east coast and Collier County on the
west coast (Mlodinow and Karlson
1999, p. 242), are expected to grow and
become more urbanized. The human
population within south Florida
surpassed 1 million (337 persons per
square mile (mi2) (130 persons per
square kilometer (km2)) in 1950, 3
million (1,013 persons per mi2 (391
persons per km2)) in 1970, and 6 million
(2,020 persons per mi2 (780 persons per
km2)) in 1990 (Service 1999c, p. 4–127).
South Florida’s human population was
projected to reach 8.2 million (2,771
persons per mi2 (1,070 persons per
km2)) by 2010 (Floyd 1996 as cited in
Service 1999c, p. 4–127). With
continuing habitat loss and human
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population growth, it is likely that
habitat within the smooth-billed ani’s
range in south Florida will continue to
be impacted.
The petition did not contain
information indicating that habitat loss
and modification are threats to the
smooth-billed ani elsewhere in its range
(i.e., outside south Florida). Throughout
its range, this species uses disturbed
and human-altered rural and suburban
areas, open areas with brush or scrub,
plantations, gardens, farmlands, forest
clearings, cow pastures, and grazing
lands with human habitation (Loflin
1983 as cited in Quinn and StartekFoote 2000, section 6, p. 1; Quinn and
Startek-Foote 2000, section 6, p. 1).
Although the landscape throughout the
smooth-billed ani’s considerable range
is undoubtedly changing, we do not
have evidence to suggest that the
species is threatened by habitat loss and
modification. In fact, ongoing
disturbance of forest habitats by humans
may create additional suitable habitat
for smooth-billed anis, suggesting the
possibility that populations are
increasing within the range of the
species (Quinn and Startek-Foote 2000,
section 11, p. 3).
Information in the petition regarding
rapid human population growth and
associated development in Florida is
supported by information in our files.
Although increased habitat loss and
human population growth may have
affected the smooth-billed ani in south
Florida, reasons for the expansion and
contraction of its range in Florida are
unclear. The species uses a wide array
of disturbed and human-altered habitats
(Quinn and Startek-Foote 2000, section
6, p. 1). Expansion in Florida may have
temporarily been facilitated by
anthropogenic habitat changes that
initially favored this species; however,
the species’ current status in Florida
may be the norm (Mlodinow and
Karlson 1999, p. 242).
We currently have no information,
and the petition provided no
information, to support a determination
that this factor is a substantial risk to the
species in south Florida or elsewhere in
its considerable range. In summary, we
find that the information provided in
the petition, as well as other
information in our files, does not
present substantial scientific or
commercial information indicating that
the petitioned action may be warranted
due to destruction, modification, or
curtailment of the smooth-billed ani’s
habitat or range, especially given that
the species uses a wide array of
disturbed habitats over a considerable
range.
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B. Overutilization for Commercial,
Recreational, Scientific, or Educational
Purposes
The petition did not present
information, nor do we have
information in our files, suggesting that
overutilization is threatening the
smooth-billed ani.
C. Disease or Predation
The petition did not provide any
information concerning disease or
predation. Information available in
Service files does not report evidence of
diseases. For instance, Quinn and
Startek-Foote (2000, section 11, p. 2),
found no reports of diseases for this
species. Two species of mallophaga
(bird lice) have been reported in the
species (Davis 1940 as cited in Quinn
and Startek-Foote 2000, section 11, p.
2). However, we do not have any
information that ties these ectoparasites
to any specific disease affecting the
smooth-billed ani. Based upon limited
information in Service files, disease is
not considered to be a threat for the
smooth-billed ani.
Evaluation of Information Provided in
the Petition and Available in Service
Files
The smooth-billed ani may be
vulnerable to predators, because it is an
awkward, slow-flying bird (Stevenson
and Anderson 1994, p. 357). However,
the species also employs a sentinel
system, with usually one individual
positioned at an open, elevated site to
warn others of predators (Loflin 1983 as
cited in Quinn and Startek-Foote 2000,
section 9, p. 4). In addition, Merritt
(1953 as cited in Stevenson and
Anderson 1994, p. 357) has postulated
that a very disagreeable odor given off
when the bird is alarmed ‘‘probably
tends to discourage predation.’’ Smoothbilled anis have been attacked or taken
by sharp-shinned hawks (Accipiter
striatus), fish crows (Corvus ossifragus),
climbing rats (Rattus rattus), and feral
cats (Felis catus) (Loflin 1983 as cited in
Quinn and Startek-Foote 2000, section
9, p. 4; Startek 1997 as cited in Quinn
and Startek-Foote 2000, section 9, p. 4;
Quinn and Startek-Foote 2000, section
9, p. 4). In a limited study, Blanchard
(2000, p. 45) noted a high incidence of
egg and chick predation, documenting
predation at 7 of 10 nests in Puerto Rico,
most likely from brown rats (Rattus
norvegicus) and feral cats. Predation
rates are not available, but group
vigilance likely limits diurnal predation
to low levels (Davis 1940 as cited in
Quinn and Startek-Foote 2000, section
11, p. 2).
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In summary, disease is not known to
be a threat to the species. Although
information on predation within our
files is limited, we do not have reason
to believe that predation is a threat to
the species. Accordingly, we find that
the information in our files does not
present substantial scientific or
commercial information indicating that
the petitioned action may be warranted
due to disease or predation.
D. The Inadequacy of Existing
Regulatory Mechanisms
The petition did not present
information, nor do we have
information in our files, suggesting that
inadequacy of existing regulatory
mechanisms is a threat to the species.
E. Other Natural or Manmade Factors
Affecting Its Continued Existence
Information Provided in the Petition
The petition suggests that one popular
explanation for the smooth-billed ani’s
recent decline in Florida may have been
periods of cold temperatures in south
Florida; however, the petition also
provides information that contradicts
this explanation. Smooth-billed anis
using the Clewiston area near Lake
Okeechobee were reported to have
survived subfreezing temperatures in
the 1940s (reportedly 28 °F in 1944 and
26 °F in 1947) (Dilley 1948, p. 314). The
petition suggests that the apparent
increase in the smooth-billed ani’s
numbers during the late 1950s and early
1960s (National Audubon Society
Christmas Bird Count data) coincides
with two cold spells, but the beginning
of the species’ decline in the early 1970s
does not correlate with a notable period
of cold weather (McGovern 2004). The
petition indicates that the severest cold
weather to hit south Florida was during
the 1980s, when smooth-billed ani
populations continued to decline, but
the species’ decline had begun before
this time.
The petition suggests that another
explanation for this species’ decline in
Florida may be hurricanes, but this also
does not seem to be reinforced by data.
The petition indicates that smoothbilled ani populations increased from
1957 to 1974, when at least five
hurricanes impacted south Florida. The
petition indicates that as populations
began to decrease in the 1970s and
1980s, south Florida was struck by only
two hurricanes (Barnes 1998).
The petition, citing Birds of North
America Online, suggests that possible
ingestion of pesticides resulting from
this species’ insect diet is another
explanation for its decline.
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The petition suggests, without
reference, that smooth-billed anis in the
United States have undergone
inexplicable natural population
fluctuations for centuries and that no
research has been conducted to
investigate this phenomenon.
Evaluation of Information Provided in
the Petition and Available in Service
Files
The Service has only limited
information regarding the possible
effects of cold temperatures on the
smooth-billed ani. The information
regarding cold temperatures as a factor
appears to be reliable based upon
limited information in Service files. The
decrease in numbers of smooth-billed
anis in south Florida from the late 1970s
through 1986 has been suggested to be
due possibly to a series of unusually
cold winters, which may have affected
birds directly or indirectly through the
reduction of the supply of insects
(Stevenson and Anderson 1994, p. 357).
Mlodinow and Karlson (1999, p. 242)
acknowledged that a series of cold
winters during the late 1970s likely
played a role (citing Robertson and
Woolfenden 1992), but suggested that a
continued decrease in the population
does not seem to be explained by
weather alone. The petition does not
present information, nor does the
Service have information in our files,
indicating that cold temperatures are a
threat to the species elsewhere in its
range.
The Service has little information
regarding the possible effects of
hurricanes on the smooth-billed ani.
The petition acknowledges that data do
not seem to reinforce the explanation
that hurricanes caused declines in south
Florida. Also, the petition does not
present information indicating that
hurricanes are a threat to the species
elsewhere in its range. In Jamaica, the
mean number of smooth-billed anis in
10 habitats before and after Hurricane
Gilbert in 1988 was not significantly
different (Wunderle et al. 1992, pp.
164–165). Similarly, no obvious decline
in smooth-billed ani abundance was
observed after Hurricane Georges in
Puerto Rico in 1998 (Quinn and StartekFoote 2000, section 11, p. 2). In general,
stochastic (random) events are not likely
to pose a significant threat to the
smooth-billed ani, due to the species’
considerable population size and
geographic range.
The information provided in the
petition regarding pesticides as a factor
appears to be reliable, based upon
limited information in Service files.
Stevenson and Anderson (1994, p. 357)
suggested that the smooth-billed ani’s
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diet of insects could result in the
ingestion of pesticides in the
agricultural areas that the species often
inhabits; they list this as an adverse
factor that may have contributed to the
smooth-billed ani’s decrease in
abundance in Florida from the late
1970s through 1986. Mlodinow and
Karlson (1999, p. 242) suggested that
pesticides may have also reduced food
sources, and that this reduction was one
possible factor contributing to the
decline in Florida. Neither the petition
nor the Service’s files present
information indicating that pesticides
are a threat to the smooth-billed ani
elsewhere in its range.
The Service has little information on
natural population fluctuations of the
smooth-billed ani in Florida or
elsewhere in its range. The petition
suggests, without reference, that
smooth-billed anis in the United States
have undergone inexplicable natural
population fluctuations for centuries
and that no research has been
conducted to investigate this
phenomenon. Based upon limited
information in our files, it appears that
the species has received relatively little
research attention. More research is
needed on the species’ mating system
and genetic relationships, reproductive
and social behaviors, habitat quality,
and foraging patterns (Quinn and
Startek-Foote 2000, section 15, p. 1).
Blanchard (2000, pp. 1–101) studied the
communal breeding system of the
species in Puerto Rico. The petition did
not present information indicating that
such natural population fluctuations are
a threat to the smooth-billed ani
elsewhere in its range. We have no
additional information to suggest that
demographic or other factors are a threat
to the smooth-billed ani in Florida or
elsewhere in its range.
Information provided by the
petitioner regarding cold temperatures,
hurricanes, pesticides, and natural
population fluctuations is generally
supported by the limited information in
our files. However, we have no
information or data that suggest that
such factors are threats to the smoothbilled ani in south Florida or elsewhere
in its range. In summary, we find that
the information provided in the
petition, as well as other information in
our files, does not present substantial
scientific or commercial information
indicating that the petitioned action
may be warranted due to natural or
anthropogenic factors, especially given
that the species appears to have a large
population over a considerable range.
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Finding
In summary, the petition does not
present substantial information, because
it does not provide specific information
on threats to the smooth-billed ani and
only alludes to possible threats within
Florida, which is a small portion of the
species’ considerable range. Information
in our files indicates that the smoothbilled ani has a large population size,
uses a wide array of disturbed habitats,
and occupies a considerable range.
While we agree with the petitioner’s
general statements about possible causes
for the species’ recent decline in
Florida, information in our files suggests
that the species’ current status in
Florida may be the norm; the species
was not known to breed in Florida prior
to the late 1930s. Neither the petition
nor our files contain information
suggesting that threats affecting the
species’ continued existence occur
elsewhere in its range.
As for the threats identified in this
petition, we found no information to
suggest that they are acting on the
smooth-billed ani such that the species
may become extinct now or in the
foreseeable future.
On the basis of our determination
under section 4(b)(3)(A) of the Act, we
conclude that the petition does not
present substantial scientific or
commercial information to indicate that
listing the smooth-billed ani under the
Act as threatened or endangered may be
warranted at this time. Although we
will not review the status of the species
at this time, we encourage interested
parties to continue to gather data that
will assist with the conservation of the
smooth-billed ani. If you wish to
provide information regarding the
smooth-billed ani, you may submit your
information or materials to the Field
Supervisor/Listing Coordinator, South
Florida Ecological Services Office (see
ADDRESSES), at any time.
References Cited
A complete list of references cited is
available on the Internet at https://
www.regulations.gov or upon request
from the South Florida Ecological
Services Office (see FOR FURTHER
INFORMATION CONTACT).
Author
The primary author of this notice is
Paula Halupa of the South Florida
Ecological Services Office (see
ADDRESSES).
Authority
The authority for this action is the
Endangered Species Act of 1973, as
amended (16 U.S.C. 1531 et seq.).
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Dated: April 13, 2011.
Rowan W. Gould,
Acting Director, U.S. Fish and Wildlife
Service.
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Agencies
[Federal Register Volume 76, Number 80 (Tuesday, April 26, 2011)]
[Proposed Rules]
[Pages 23265-23271]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2011-9975]
-----------------------------------------------------------------------
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[Docket No. FWS-R4-ES-2011-0007; MO 92210-0-0008]
Endangered and Threatened Wildlife and Plants; 90-Day Finding on
a Petition To List the Smooth-Billed Ani as Threatened or Endangered
AGENCY: Fish and Wildlife Service, Interior.
ACTION: Notice of 90-day petition finding.
-----------------------------------------------------------------------
SUMMARY: We, the U.S. Fish and Wildlife Service, announce a 90-day
finding on a petition to list the smooth-billed ani (Crotophaga ani) as
threatened or endangered under the Endangered Species Act of 1973, as
amended (Act). Based on our review, we find that the petition does not
present substantial information indicating that listing the species may
be warranted. Therefore, we are not initiating a status review in
response to this petition. However, we ask the public to submit to us
any new information that becomes available concerning the status of, or
threats to, the smooth-billed ani or its habitat at any time.
DATES: The finding announced in this document was made on April 26,
2011.
ADDRESSES: This finding is available on the Internet at https://www.regulations.gov at Docket Number FWS-R4-ES-2011-0007. 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, South Florida Ecological Services Office,
1339 20th Street, Vero Beach, Florida 32960-3559. Please submit any new
information, materials, comments, or questions concerning this finding
to the above address.
FOR FURTHER INFORMATION CONTACT: Spencer Simon, Assistant Field
Supervisor, of the South Florida Ecological Services Office (see
ADDRESSES) by telephone 772-562-3909, or by facsimile to 772-562-4288.
If you use a telecommunications device for the deaf (TDD), please call
the Federal Information Relay Service (FIRS) at 800-877-8339.
SUPPLEMENTARY INFORMATION:
Background
Section 4(b)(3)(A) of the Act (16 U.S.C. 1531 et seq.) requires
that we make a finding on whether a petition to
[[Page 23266]]
list, delist, or reclassify a species presents substantial scientific
or commercial information indicating that the petitioned action may be
warranted. We are to base this finding on information provided in the
petition, supporting information submitted with the petition, and
information otherwise available in our files. To the maximum extent
practicable, we are to make this finding within 90 days of our receipt
of the petition and publish our notice of the finding promptly in the
Federal Register.
Our standard for substantial scientific or commercial information
within the Code of Federal Regulations (CFR) with regard to a 90-day
petition finding is ``that amount of information that would lead a
reasonable person to believe that the measure proposed in the petition
may be warranted'' (50 CFR 424.14(b)). If we find that substantial
scientific or commercial information was presented, we are required to
promptly conduct a species status review, which we subsequently
summarize in our 12-month finding.
Petition History
On April 5, 2005, we received a petition, dated March 23, 2005,
from Robert Showler of Homestead, Florida, requesting that the smooth-
billed ani (Crotophaga ani), a bird, be listed as endangered under the
Act. The petition clearly identified itself as such and included the
requisite identification information for the petitioner(s), as required
by 50 CFR 424.14(a). In an April 29, 2005, letter to the petitioner, we
responded that we received the petition for the smooth-billed ani, and
that because of inadequate funding for listing-related actions pursuant
to court orders and judicially approved settlement agreements, we would
not be able to address the petition at that time. We also noted that
the species had been included on the list of birds of conservation
concern in peninsular Florida in 2002 and that we had begun to compile
information on this and other species of conservation concern in
peninsular Florida. This finding addresses the petition.
Species Information
The smooth-billed ani (Crotophaga ani) is a member of the Family
Cuculidae (cuckoo family). We concur with the petition's taxonomic
characterization of the smooth-billed ani (Crotophaga ani) as a
species. This species is a resident in parts of Florida, the Caribbean,
Mexico, and Central and South America (Stevenson and Anderson 1994, p.
355; Quinn and Startek-Foote 2000, section 3, p. 1). The smooth-billed
ani is a medium-sized cuculid, with a length of 12-14 inches (30-36
centimeters) and a mass of approximately 3.5 ounces (100 grams)
(Ridgway 1916 and Loflin 1983 as cited in Quinn and Startek-Foote 2000,
section 2, p. 1). Males tend to be slightly larger than females (Quinn
and Startek-Foote 2000, section 2, p. 1). This species is distinguished
by: all-black plumage, glossed with greenish or violet iridescence in
parts; a long tail (approximately 6.8 in (17.2 cm)); a large, arched,
and laterally compressed bill, usually showing a raised hump on the
basal half of the upper mandible; and a distinctive call, including a
whining ``ah-nee,'' which is usually delivered 1-4 times, along with
other vocalizations (Quinn and Startek-Foote 2000, section 1, p. 1;
section 2, p. 1; section 8, p. 1). Immature birds resemble adults, but
their plumage contains a mixture of dull and glossy blackish feathers,
and the bill is slightly shallower (Quinn and Startek-Foote 2000,
section 2, p. 1). Juveniles are also similar in appearance to adults,
but with plumage that is entirely dull blackish in color with little or
no gloss, and a smaller bill without a raised hump (Quinn and Startek-
Foote 2000, section 2, p. 1).
The smooth-billed ani occurs over a considerable global geographic
range. It is considered a resident from central Florida south through
the Caribbean, and south into Central and South America through Ecuador
and northern Argentina, except in the Andes (Stevenson and Anderson
1994, p. 355; Quinn and Startek-Foote 2000, section 3, p. 1). The
species is generally nonmigratory; however, some local movement occurs
during the dry season, when many groups leave their territories and
gather in large flocks with neighboring groups (Loflin 1983 as cited in
Quinn and Startek-Foote 2000, section 5, p. 1). Records in the Dry
Tortugas suggest some movement between the Caribbean and Florida
(Robertson and Woolfenden 1992 as cited in Mlodinow and Karlson 1999,
p. 241). This species may regularly disperse from the Bahamas and Cuba
to Florida (Mlodinow and Karlson 1999, p. 242). The smooth-billed ani
has been described as a casual occurrence north to North Carolina and
west to Louisiana (Stevenson and Anderson 1994, p. 355). Vagrant
records elsewhere in the United States are scarce; few acceptable
records outside of Florida exist (e.g., New Jersey or Pennsylvania,
North Carolina, South Carolina, and Georgia) (Mlodinow and Karlson
1999, pp. 241-242).
Throughout its range, and year round, the smooth-billed ani
occupies savanna, disturbed and human-altered rural and suburban areas,
open areas with brush or scrub, plantations, gardens, farmlands, and
forest clearings (Quinn and Startek-Foote 2000, section 6, p. 1).
Preferred habitat is considered to be open grassland (Blanchard 2000,
p. 5). In Puerto Rico, Guyana, Cuba, Jamaica, Colombia, and the
Gal[aacute]pagos Islands, this species uses cow pastures and adjacent
lands (Quinn and Startek-Foote 2000, section 6, p. 1). In south
Florida, density was positively correlated with amount of grazing lands
and human habitation (Loflin 1983 as cited in Quinn and Startek-Foote
2000, section 6, p. 1). In general, this species typically occupies
lowlands, often near the coast, preferring a source of water (e.g.,
marsh, pond, river) and avoiding dense forest (Quinn and Startek-Foote
2000, section 6, p. 1). In a study area in south Florida, the smooth-
billed ani was found to occupy discontinuous patches of habitat (e.g.,
parks, nurseries, small undeveloped plots of land) and avoid tall
grasses of the Everglades (Loflin 1983 as cited in Quinn and Startek-
Foote 2000, section 6, p. 1). Additionally, the species has been found
within and near impoundments within the Loxahatchee National Wildlife
Refuge (NWR) (Service 1997, p. 48; 1998, p. 50; 1999a, p. 65; 2003a,
pp. 113-114) and on various outer islands within the Florida Keys NWR
Complex (Service 1992, p. 85; 1999b, p. 60; 2001, p. 69; 2003b, p. 84).
This species feeds primarily on insects and small vertebrates,
especially when these forage items are abundant during the rainy
season; fruit is an important component of the diet during the dry
season (Quinn and Startek-Foote 2000, section 1, p. 1 and section 7,
pp. 1-2; Blanchard 2000, p. 5). Fields of grass are typically used for
foraging; more densely vegetated stream edges may be used for nesting
and roosting (Quinn and Startek-Foote 2000, section 6, p. 1; Blanchard
2000, p. 5). The smooth-billed ani is a highly social bird that nests,
roosts, feeds, and travels in pairs or in communal groups (Quinn and
Startek-Foote 2000, section 9, p. 3; Blanchard 2000, pp. 5-6). This
species uses a communal breeding system in which a number of females
lay eggs and incubate in the same nest; late-laying females bury the
eggs of early-laying females with twigs and leaves, which can create a
number of layers, but only the top layer of eggs eventually hatches
(Quinn and Startek-Foote 2000, section 1, p. 1; Blanchard 2000, pp. 1-
101). Blanchard (2000, p. 30) found evidence for monogamy, polygamy
(extra-pair fertilizations), and brood parasitism (egg-laying in the
nests of other birds) in
[[Page 23267]]
both single-pair and group nests in a study of the species' communal
breeding system in Puerto Rico. Observed nesting groups of smooth-
billed anis ranged from a single pair to 12 adults and nests containing
more than 30 eggs (Blanchard 2000, p. 11). Female-female competition at
the nest may result in the destruction of other females' eggs through
egg burial under nesting material (Blanchard 2000, p. 11).
The smooth-billed ani has a large global population, estimated in
2004 to be 20,000,000 individuals, with less than or equal to 1 percent
occurring in the United States (Rich et al. 2004, p. 70). Global long-
term trend data did not exist at that time (Rich et al. 2004, p. 70).
In general, little information on global population size or trends was
available in Service files at the time the petition was received.
Available information suggested that the smooth-billed ani's
conservation status was ``not threatened'' (Quinn and Startek-Foote
2000, section 12, p. 1). The species was not recognized as a National
Audubon Society Watch List Species or Stewardship Species (Rich et al.
2004, p. 70). The Audubon Watch List categorizes species on the list if
they are declining rapidly and/or have very small populations or
limited ranges and face major conservation threats (e.g., typically
species of global conservation concern) or if the species are either
declining or rare (e.g., typically species of national conservation
concern).
The smooth-billed ani is an uncommon-to-rare resident of southern
Florida (Mlodinow and Karlson 1999, p. 241). Prior to the 1930s, few
records existed in Florida, suggesting that the species was rare or
poorly known (Quinn and Startek-Foote 2000, section 3, p. 2). Sprunt
(1939, pp. 335-336) documented the first record of breeding in Florida
in 1938. By the late 1930s, the species was considered established in
the Lake Okeechobee area, and subsequently breeding was recorded
elsewhere in south Florida (Quinn and Startek-Foote 2000, section 3, p.
2). The species' status in Florida remained relatively unchanged until
the 1960s, when increasing numbers were recorded in central and north
Florida (Quinn and Startek-Foote 2000, section 3, p. 2). Based upon
National Audubon Society Christmas Bird Counts, the number observed per
party hour (p-hr) (average number of counts per party per hour spent
censusing) tripled by 1962-63, reaching 0.17 per p-hr in West Palm
Beach and 2.41 per p-hr in Fort Lauderdale (Mlodinow and Karlson 1999,
p. 241). In the 1960s the species was fairly common to common from the
Everglades north to Brevard County on the east coast and Lee County on
the west coast (Mlodinow and Karlson 1999, p. 241). By 1968-69, the
number observed reached 1.51 per p-hr in West Palm Beach and 4.20 per
p-hr in Fort Lauderdale (Mlodinow and Karlson 1999, p. 241).
Numbers appeared to have peaked in Florida during the period 1968-
1976, when the species was recorded north to Jacksonville Beach (Duval
County) in the east and St. Petersburg (Hillsborough County) in the
west (Mlodinow and Karlson 1999, p. 241; Quinn and Startek-Foote 2000,
section 3, p. 2). At that time, numbers observed were typically in the
3.0-4.0 per p-hr range in Fort Lauderdale, while Fort Pierce reached
1.87 per p-hr and Sanibel Island/Captiva Island reached 0.41 per p-hr
(Mlodinow and Karlson 1999, p. 241). By winter 1977-1978, numbers had
declined sharply, returning to mid-1960s levels (Mlodinow and Karlson
1999, p. 241). This decline continued, and by 1988-1989, total numbers
were comparable to those reported in the 1950s (Mlodinow and Karlson
1999, p. 241). The decline continued in Florida into the 1990s, and by
1998, the smooth-billed ani was found locally from the Florida Keys
north to West Palm Beach on the east coast, and north to Collier County
on the west coast (Mlodinow and Karlson 1999, pp. 241-242). Mlodinow
and Karlson (1999, p. 242) suggested that the status of the smooth-
billed ani in Florida in 1998 may be the norm rather than an
aberration.
Available information in Service files suggests that the species
uses Loxahatchee NWR (Service, annual narrative reports from 1996 to
2005) and the Florida Keys NWR Complex (Service, annual narrative
reports from 1939 to 2003). According to a notation in the 2000 annual
narrative report from Loxahatchee NWR, local long-time birders have
indicated that the numbers of smooth-billed anis in south Florida and
on the Refuge have declined significantly and that annual Christmas
Bird Counts are showing the same trend (Service 2000, p. 110).
The reasons for expansion and contraction of the species' range in
Florida are not known. Expansion may have been facilitated by
residential development, which resulted in anthropogenic habitat
changes that initially favored this species (Mlodinow and Karlson 1999,
p. 242). However, continued residential and agricultural development,
which reduced suitable habitat, and exceptionally cold winters during
the 1970s may have contributed to subsequent declines (Stevenson and
Anderson 1994, p. 357; Mlodinow and Karlson 1999, p. 242). Overall, the
reasons for the decline in south Florida are not clear (Mlodinow and
Karlson 1999, p. 242; National Audubon Society 2001, p. 335).
The smooth-billed ani was one of 668 taxa evaluated in an effort to
help prioritize vertebrate conservation efforts in Florida (Millsap et
al. 1990, pp. 3-57). The evaluation system ranked taxa (species and
subspecies) according to biological vulnerability, extent of current
knowledge of population status, and management needs (Millsap et al.
1990, pp. 3-57). During this ranking process, the smooth-billed ani was
not considered to be an imperiled taxon in Florida as indicated from
its biological score, which was based upon facets of its distribution,
abundance, and life history (Millsap et al. 1990, pp. 28-29).
Information available in Service files at the time the petition was
received indicated that, in 2002, the Service's Division of Migratory
Bird Management included the smooth-billed ani as a bird of
conservation concern in peninsular Florida in its report, entitled
``Birds of Conservation Concern 2002'' (Service 2002, p. 68). The
purpose of the report was to identify migratory and nonmigratory birds
of the United States and its territories that are of conservation
concern to encourage coordinated and proactive conservation actions
among Federal, State, and private partners (Service 2002, p. 3). The
overall goal of that report was to accurately identify the migratory
and nonmigratory bird species (beyond those already designated as
federally threatened or endangered) that represented the Service's
highest conservation priorities and draw attention to species in need
of conservation action (Service 2002, p. 3). The geographic scope of
this endeavor comprised the United States in its entirety, including
island ``territories'' in the Pacific and Caribbean (Service 2002, p.
1). Although the smooth-billed ani was identified as one of 78 birds of
conservation concern in the Southeast, only the U.S. mainland portion
of the Region was identified as of concern; Puerto Rico and the U.S.
Virgin Islands were not identified as of concern (Service 2002, p. 68).
In addition, the report does not include foreign countries.
Evaluation of Information for This Finding
Section 4 of the Act (16 U.S.C. 1533) and its implementing
regulations at 50 CFR part 424 set forth the procedures for adding a
species to, or removing a species from, the Federal Lists of Endangered
and Threatened Wildlife and Plants. A species may be
[[Page 23268]]
determined to be an endangered or threatened species due to one or more
of the five factors described in section 4(a)(1) of the Act:
(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 considering what factors might constitute threats, we must look
beyond the mere exposure of the species to the factor to determine
whether the species responds to the factor in a way that causes actual
impacts to the species. If there is exposure to a factor, but no
response, or only a positive response, that factor is not a threat. If
there is exposure and the species responds negatively, the factor may
be a threat and we then attempt to determine how significant a threat
it is. If the threat is significant, it may drive or contribute to the
risk of extinction of the species such that the species may warrant
listing as threatened or endangered as those terms are defined by the
Act. This does not necessarily require empirical proof of a threat. The
combination of exposure and some corroborating evidence of how the
species is likely impacted could suffice. The mere identification of
factors that could impact a species negatively may not be sufficient to
compel a finding that listing may be warranted. The information shall
contain evidence sufficient to suggest that these factors may be
operative threats that act on the species to the point that the species
may meet the definition of threatened or endangered under the Act.
In making this 90-day finding, we evaluated whether information
regarding the threats to the smooth-billed ani, as presented in the
petition and other information available in our files, is substantial,
thereby indicating that the petitioned action may be warranted. Our
evaluation of this information is presented below.
A. The Present or Threatened Destruction, Modification, or Curtailment
of Its Habitat or Range
Information Provided in the Petition
The petition acknowledges that the smooth-billed ani's historic
range in the United States has largely been restricted to southern
Florida (Bent 1940; Terres 1980, p. 146) and that the species is
considered common in many parts of its range throughout the Caribbean,
including the Bahamas. The petition states that numerous records in the
Dry Tortugas during the last 150 years indicate that the species is
capable of traveling from Cuba to Florida (Birds of North America
Online). The petition indicates that the species was reported in low
numbers in Florida during the 1800s and early 1900s (Sprunt 1932; Bent
1940), with the first report of breeding in Florida in 1938 (Sprunt
1932; Terres 1980, p. 146). It also cites records from Louisiana and
North Carolina dating back to the early 1800s (Bent 1940). The petition
suggests that the species seems to have experienced an increase in
population from the late 1950s through the early 1970s, and then a
rapid decline from the 1970s to 2005. The petition claims that smooth-
billed anis are extremely rare everywhere in the United States, noting
data from various National Audubon Society Christmas Bird Counts.
The petition indicates that the species generally prefers ``open''
habitats, such as weedy and shrubby fields, pastures, farmland, and
occasionally residential areas. Based upon a variety of unspecified
sources, the petition states that the species is not commonly found in
heavily forested or extensive marshes.
The petition states that rapid human population growth and
associated development throughout peninsular Florida, much of it
occurring within the species' preferred habitat and historic range, may
be a potential contributor to the decline of the smooth-billed ani. The
petition provides the following statement: ``Apparently [the ani is]
declining as southern Florida continues to develop, and the brushland
shrub/scrub habitat is lost (Alsop 2002).'' No additional information
or citations relating to habitat loss as a threat are given in the
petition.
Evaluation of Information Provided in the Petition and Available in
Service Files
The smooth-billed ani appears to have declined from previous high
levels in Florida (Stevenson and Anderson 1994, pp. 356-357; Mlodinow
and Karlson 1999, p. 242; National Audubon Society 2005, pp. 1-3).
However, it has been suggested that this species' current status in
Florida may be the norm rather than an aberration (Mlodinow and Karlson
1999, p. 242). It was not until 1938 that the species was established
and breeding in Florida (Sprunt 1939, pp. 335-336; Stevenson and
Anderson 1994, p. 355). One hypothesis suggests that prior to the World
War I era, south Florida had little suitable smooth-billed ani habitat,
since it was largely a wetland surrounded by an inner zone of pine
forests and outer zones of mangroves and sandy beaches (Mlodinow and
Karlson 1999, p. 242). Substantial anthropogenic changes beginning in
the 1920s, consisting of agricultural development and low-level
residential development, may have created enough suitable habitat for
dispersing anis to successfully colonize south Florida in the 1930s
(Mlodinow and Karlson 1999, p. 242). Over time, residential development
increased and more intensive agricultural practices and other factors
may have reduced suitable habitat and dispersal habitat, causing
decreased reproductive success and lower recruitment (Mlodinow and
Karlson 1999, p. 242). Alsop (2002, p. 212) noted that the smooth-
billed ani is apparently declining in south Florida as the area
continues to develop and brushland shrub/scrub habitat is lost.
Information in our files supports the statement in the petition
that human population growth and associated land-use changes are
occurring in peninsular Florida, and that additional growth is expected
in the future. In the 50 years prior to 1994, more than 8 million acres
[(3.24 million hectares (ha)] of forest and wetland habitats (roughly
24 percent of the State) were cleared to accommodate an expanding human
population (Cox et al. 1994, p. i). Statewide, between 1936 and 1987,
cropland and rangeland increased by 4.25 million acres (1.72 million
ha), or 30 percent; urban areas increased by 3.95 million acres (1.60
million ha), or 538 percent; herbaceous wetlands declined by 3.88
million acres (1.57 million ha), or 56 percent; and forests declined by
4.30 million acres (1.74 million ha), or 21 percent (Service 1999c, p.
4-128).
Although some anthropogenic habitat changes may initially favor
this species, areas where the smooth-billed ani can be locally found in
Florida, from the Keys north to West Palm Beach on the east coast and
Collier County on the west coast (Mlodinow and Karlson 1999, p. 242),
are expected to grow and become more urbanized. The human population
within south Florida surpassed 1 million (337 persons per square mile
(mi\2\) (130 persons per square kilometer (km\2\)) in 1950, 3 million
(1,013 persons per mi\2\ (391 persons per km\2\)) in 1970, and 6
million (2,020 persons per mi\2\ (780 persons per km\2\)) in 1990
(Service 1999c, p. 4-127). South Florida's human population was
projected to reach 8.2 million (2,771 persons per mi\2\ (1,070 persons
per km\2\)) by 2010 (Floyd 1996 as cited in Service 1999c, p. 4-127).
With continuing habitat loss and human
[[Page 23269]]
population growth, it is likely that habitat within the smooth-billed
ani's range in south Florida will continue to be impacted.
The petition did not contain information indicating that habitat
loss and modification are threats to the smooth-billed ani elsewhere in
its range (i.e., outside south Florida). Throughout its range, this
species uses disturbed and human-altered rural and suburban areas, open
areas with brush or scrub, plantations, gardens, farmlands, forest
clearings, cow pastures, and grazing lands with human habitation
(Loflin 1983 as cited in Quinn and Startek-Foote 2000, section 6, p. 1;
Quinn and Startek-Foote 2000, section 6, p. 1). Although the landscape
throughout the smooth-billed ani's considerable range is undoubtedly
changing, we do not have evidence to suggest that the species is
threatened by habitat loss and modification. In fact, ongoing
disturbance of forest habitats by humans may create additional suitable
habitat for smooth-billed anis, suggesting the possibility that
populations are increasing within the range of the species (Quinn and
Startek-Foote 2000, section 11, p. 3).
Information in the petition regarding rapid human population growth
and associated development in Florida is supported by information in
our files. Although increased habitat loss and human population growth
may have affected the smooth-billed ani in south Florida, reasons for
the expansion and contraction of its range in Florida are unclear. The
species uses a wide array of disturbed and human-altered habitats
(Quinn and Startek-Foote 2000, section 6, p. 1). Expansion in Florida
may have temporarily been facilitated by anthropogenic habitat changes
that initially favored this species; however, the species' current
status in Florida may be the norm (Mlodinow and Karlson 1999, p. 242).
We currently have no information, and the petition provided no
information, to support a determination that this factor is a
substantial risk to the species in south Florida or elsewhere in its
considerable range. In summary, we find that the information provided
in the petition, as well as other information in our files, does not
present substantial scientific or commercial information indicating
that the petitioned action may be warranted due to destruction,
modification, or curtailment of the smooth-billed ani's habitat or
range, especially given that the species uses a wide array of disturbed
habitats over a considerable range.
B. Overutilization for Commercial, Recreational, Scientific, or
Educational Purposes
The petition did not present information, nor do we have
information in our files, suggesting that overutilization is
threatening the smooth-billed ani.
C. Disease or Predation
The petition did not provide any information concerning disease or
predation. Information available in Service files does not report
evidence of diseases. For instance, Quinn and Startek-Foote (2000,
section 11, p. 2), found no reports of diseases for this species. Two
species of mallophaga (bird lice) have been reported in the species
(Davis 1940 as cited in Quinn and Startek-Foote 2000, section 11, p.
2). However, we do not have any information that ties these
ectoparasites to any specific disease affecting the smooth-billed ani.
Based upon limited information in Service files, disease is not
considered to be a threat for the smooth-billed ani.
Evaluation of Information Provided in the Petition and Available in
Service Files
The smooth-billed ani may be vulnerable to predators, because it is
an awkward, slow-flying bird (Stevenson and Anderson 1994, p. 357).
However, the species also employs a sentinel system, with usually one
individual positioned at an open, elevated site to warn others of
predators (Loflin 1983 as cited in Quinn and Startek-Foote 2000,
section 9, p. 4). In addition, Merritt (1953 as cited in Stevenson and
Anderson 1994, p. 357) has postulated that a very disagreeable odor
given off when the bird is alarmed ``probably tends to discourage
predation.'' Smooth-billed anis have been attacked or taken by sharp-
shinned hawks (Accipiter striatus), fish crows (Corvus ossifragus),
climbing rats (Rattus rattus), and feral cats (Felis catus) (Loflin
1983 as cited in Quinn and Startek-Foote 2000, section 9, p. 4; Startek
1997 as cited in Quinn and Startek-Foote 2000, section 9, p. 4; Quinn
and Startek-Foote 2000, section 9, p. 4). In a limited study, Blanchard
(2000, p. 45) noted a high incidence of egg and chick predation,
documenting predation at 7 of 10 nests in Puerto Rico, most likely from
brown rats (Rattus norvegicus) and feral cats. Predation rates are not
available, but group vigilance likely limits diurnal predation to low
levels (Davis 1940 as cited in Quinn and Startek-Foote 2000, section
11, p. 2).
In summary, disease is not known to be a threat to the species.
Although information on predation within our files is limited, we do
not have reason to believe that predation is a threat to the species.
Accordingly, we find that the information in our files does not present
substantial scientific or commercial information indicating that the
petitioned action may be warranted due to disease or predation.
D. The Inadequacy of Existing Regulatory Mechanisms
The petition did not present information, nor do we have
information in our files, suggesting that inadequacy of existing
regulatory mechanisms is a threat to the species.
E. Other Natural or Manmade Factors Affecting Its Continued Existence
Information Provided in the Petition
The petition suggests that one popular explanation for the smooth-
billed ani's recent decline in Florida may have been periods of cold
temperatures in south Florida; however, the petition also provides
information that contradicts this explanation. Smooth-billed anis using
the Clewiston area near Lake Okeechobee were reported to have survived
subfreezing temperatures in the 1940s (reportedly 28 [deg]F in 1944 and
26 [deg]F in 1947) (Dilley 1948, p. 314). The petition suggests that
the apparent increase in the smooth-billed ani's numbers during the
late 1950s and early 1960s (National Audubon Society Christmas Bird
Count data) coincides with two cold spells, but the beginning of the
species' decline in the early 1970s does not correlate with a notable
period of cold weather (McGovern 2004). The petition indicates that the
severest cold weather to hit south Florida was during the 1980s, when
smooth-billed ani populations continued to decline, but the species'
decline had begun before this time.
The petition suggests that another explanation for this species'
decline in Florida may be hurricanes, but this also does not seem to be
reinforced by data. The petition indicates that smooth-billed ani
populations increased from 1957 to 1974, when at least five hurricanes
impacted south Florida. The petition indicates that as populations
began to decrease in the 1970s and 1980s, south Florida was struck by
only two hurricanes (Barnes 1998).
The petition, citing Birds of North America Online, suggests that
possible ingestion of pesticides resulting from this species' insect
diet is another explanation for its decline.
[[Page 23270]]
The petition suggests, without reference, that smooth-billed anis
in the United States have undergone inexplicable natural population
fluctuations for centuries and that no research has been conducted to
investigate this phenomenon.
Evaluation of Information Provided in the Petition and Available in
Service Files
The Service has only limited information regarding the possible
effects of cold temperatures on the smooth-billed ani. The information
regarding cold temperatures as a factor appears to be reliable based
upon limited information in Service files. The decrease in numbers of
smooth-billed anis in south Florida from the late 1970s through 1986
has been suggested to be due possibly to a series of unusually cold
winters, which may have affected birds directly or indirectly through
the reduction of the supply of insects (Stevenson and Anderson 1994, p.
357). Mlodinow and Karlson (1999, p. 242) acknowledged that a series of
cold winters during the late 1970s likely played a role (citing
Robertson and Woolfenden 1992), but suggested that a continued decrease
in the population does not seem to be explained by weather alone. The
petition does not present information, nor does the Service have
information in our files, indicating that cold temperatures are a
threat to the species elsewhere in its range.
The Service has little information regarding the possible effects
of hurricanes on the smooth-billed ani. The petition acknowledges that
data do not seem to reinforce the explanation that hurricanes caused
declines in south Florida. Also, the petition does not present
information indicating that hurricanes are a threat to the species
elsewhere in its range. In Jamaica, the mean number of smooth-billed
anis in 10 habitats before and after Hurricane Gilbert in 1988 was not
significantly different (Wunderle et al. 1992, pp. 164-165). Similarly,
no obvious decline in smooth-billed ani abundance was observed after
Hurricane Georges in Puerto Rico in 1998 (Quinn and Startek-Foote 2000,
section 11, p. 2). In general, stochastic (random) events are not
likely to pose a significant threat to the smooth-billed ani, due to
the species' considerable population size and geographic range.
The information provided in the petition regarding pesticides as a
factor appears to be reliable, based upon limited information in
Service files. Stevenson and Anderson (1994, p. 357) suggested that the
smooth-billed ani's diet of insects could result in the ingestion of
pesticides in the agricultural areas that the species often inhabits;
they list this as an adverse factor that may have contributed to the
smooth-billed ani's decrease in abundance in Florida from the late
1970s through 1986. Mlodinow and Karlson (1999, p. 242) suggested that
pesticides may have also reduced food sources, and that this reduction
was one possible factor contributing to the decline in Florida. Neither
the petition nor the Service's files present information indicating
that pesticides are a threat to the smooth-billed ani elsewhere in its
range.
The Service has little information on natural population
fluctuations of the smooth-billed ani in Florida or elsewhere in its
range. The petition suggests, without reference, that smooth-billed
anis in the United States have undergone inexplicable natural
population fluctuations for centuries and that no research has been
conducted to investigate this phenomenon. Based upon limited
information in our files, it appears that the species has received
relatively little research attention. More research is needed on the
species' mating system and genetic relationships, reproductive and
social behaviors, habitat quality, and foraging patterns (Quinn and
Startek-Foote 2000, section 15, p. 1). Blanchard (2000, pp. 1-101)
studied the communal breeding system of the species in Puerto Rico. The
petition did not present information indicating that such natural
population fluctuations are a threat to the smooth-billed ani elsewhere
in its range. We have no additional information to suggest that
demographic or other factors are a threat to the smooth-billed ani in
Florida or elsewhere in its range.
Information provided by the petitioner regarding cold temperatures,
hurricanes, pesticides, and natural population fluctuations is
generally supported by the limited information in our files. However,
we have no information or data that suggest that such factors are
threats to the smooth-billed ani in south Florida or elsewhere in its
range. In summary, we find that the information provided in the
petition, as well as other information in our files, does not present
substantial scientific or commercial information indicating that the
petitioned action may be warranted due to natural or anthropogenic
factors, especially given that the species appears to have a large
population over a considerable range.
Finding
In summary, the petition does not present substantial information,
because it does not provide specific information on threats to the
smooth-billed ani and only alludes to possible threats within Florida,
which is a small portion of the species' considerable range.
Information in our files indicates that the smooth-billed ani has a
large population size, uses a wide array of disturbed habitats, and
occupies a considerable range. While we agree with the petitioner's
general statements about possible causes for the species' recent
decline in Florida, information in our files suggests that the species'
current status in Florida may be the norm; the species was not known to
breed in Florida prior to the late 1930s. Neither the petition nor our
files contain information suggesting that threats affecting the
species' continued existence occur elsewhere in its range.
As for the threats identified in this petition, we found no
information to suggest that they are acting on the smooth-billed ani
such that the species may become extinct now or in the foreseeable
future.
On the basis of our determination under section 4(b)(3)(A) of the
Act, we conclude that the petition does not present substantial
scientific or commercial information to indicate that listing the
smooth-billed ani under the Act as threatened or endangered may be
warranted at this time. Although we will not review the status of the
species at this time, we encourage interested parties to continue to
gather data that will assist with the conservation of the smooth-billed
ani. If you wish to provide information regarding the smooth-billed
ani, you may submit your information or materials to the Field
Supervisor/Listing Coordinator, South Florida Ecological Services
Office (see ADDRESSES), at any time.
References Cited
A complete list of references cited is available on the Internet at
https://www.regulations.gov or upon request from the South Florida
Ecological Services Office (see FOR FURTHER INFORMATION CONTACT).
Author
The primary author of this notice is Paula Halupa of the South
Florida Ecological Services Office (see ADDRESSES).
Authority
The authority for this action is the Endangered Species Act of
1973, as amended (16 U.S.C. 1531 et seq.).
[[Page 23271]]
Dated: April 13, 2011.
Rowan W. Gould,
Acting Director, U.S. Fish and Wildlife Service.
[FR Doc. 2011-9975 Filed 4-25-11; 8:45 am]
BILLING CODE 4310-55-P