Federal Register, Volume 77 Issue 247 (Wednesday, December 26, 2012) 2012 Federal Register, 77 FR 75947-75966; Centralized Library: U.S. Fish and Wildlife Service -

[Federal Register Volume 77, Number 247 (Wednesday, December 26, 2012)]
[Proposed Rules]
[Pages 75947-75966]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2012-30731]

[[Page 75947]]

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DEPARTMENT OF THE INTERIOR

Fish and Wildlife Service

50 CFR Part 17

[Docket No. FWS-R4-ES-2011-0020; 92220-1113-0000-C6]
RIN 1018-AX60

Endangered and Threatened Wildlife and Plants; Reclassification
of the Continental U.S. Breeding Population of the Wood Stork From
Endangered to Threatened

AGENCY: Fish and Wildlife Service, Interior.

ACTION: Proposed rule and notice of petition finding.

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SUMMARY: We, the U.S. Fish and Wildlife Service (Service or USFWS),
propose to reclassify the continental United States (U.S.) breeding
population of wood stork from endangered to threatened under the
Endangered Species Act of 1973, as amended (Act). We find that the best
available scientific and commercial data indicate that the endangered
designation no longer correctly reflects the current status of the
continental U.S. breeding population of the wood stork due to a
substantial improvement in the species' overall status. This proposed
rule also constitutes our 12-month finding on the petition to
reclassify the species.

DATES: We will accept comments on this proposed rule received or
postmarked on or before February 25, 2013. We must receive requests for
a public hearing, in writing at the address shown in the FOR FURTHER
INFORMATION CONTACT section, by February 11, 2013.

ADDRESSES: You may submit comments by one of the following methods:
Federal eRulemaking Portal: http://www.regulations.gov.
Follow the instructions for submitting comments on Docket No. FWS-R4-
ES-2011-0020.
U.S. mail or hand-delivery: Public Comments Processing,
Attn: FWS-R4-ES-2011-0020; Division of Policy and Directives
Management; U.S. Fish and Wildlife Service; 4401 N. Fairfax Drive,
Suite 222; Arlington, VA 22203.
We will post all comments on http://www.regulations.gov. This
generally means that we will post any personal information you provide
us (see the Public Comments section below for more information).

FOR FURTHER INFORMATION CONTACT: Field Supervisor, North Florida
Ecological Services Field Office, 7915 Baymeadows Way, Suite 200,
Jacksonville, FL 32256; telephone 904-731-3336; facsimile 904-731-3045.
If you use a telecommunications device for the deaf (TDD), please call
the Federal Information Relay Service (FIRS) at 800-877-8339, 24 hours
a day, 7 days a week.

SUPPLEMENTARY INFORMATION:

Executive Summary

Why We Need To Publish a Rule

In September 2007, we completed a 5-year status review,
which included a recommendation to reclassify the continental U.S.
breeding population of the wood stork from endangered to threatened.
In May 2009, we received a petition to reclassify the
continental U.S. breeding population of wood stork; the petition
incorporated the Service's 5-year review as its sole supporting
information.
On September 21, 2010, we published a 90-day finding that
the petition presented substantial information indicating that
reclassifying the wood stork may be warranted (75 FR 57426).
This proposed rule, in accordance with section 4(b)(3)(B)
of the Endangered Species Act (Act), constitutes our 12-month finding
on the petition we received.

Summary of the Major Provisions of This Proposed Rule

We propose to reclassify the continental U.S. breeding
population of wood stork from endangered to threatened.
This proposed rule constitutes our 12-month petition
finding.
We determine that the continental U.S. breeding population
of wood stork meets the criteria of a distinct population segment (DPS)
under our 1996 DPS policy (61 FR 4722).
We propose to amend the List of Endangered and Threatened
Wildlife (50 CFR 17.11(h)) to reflect that the U.S. wood stork DPS is
found in the States of Florida, Georgia, South Carolina, North
Carolina, Alabama, and Mississippi.

The Basis for Our Action

The continental U.S. breeding population of wood stork was
listed under the Act in 1984, prior to publication of the joint policy
of the National Marine Fisheries Service and U.S. Fish and Wildlife
Service (Services) regarding the recognition of distinct vertebrate
population segments (61 FR 4722). We find that the continental U.S.
breeding population of wood stork meets the discreteness and
significance elements of the Services' DPS policy and is a valid DPS.
When the continental U.S. breeding population of wood
stork was listed in 1984, the population was known to occur only in
Florida, Georgia, South Carolina, and Alabama. Based on new information
about where the population is found and where nesting is occurring, the
population is now known to occur in North Carolina and Mississippi in
addition to Florida, Georgia, South Carolina, and Alabama.
The best available scientific and commercial data indicate
that since the continental U.S. breeding population of wood stork was
listed as endangered in 1984, the population has been increasing and
its breeding range has expanded significantly.
Downlisting criteria from the recovery plan have been met
or exceeded. We have had 3-year population averages of total nesting
pairs of wood storks higher than 6,000 nesting pairs since 2003.
However, the 5-year average number of nesting pairs is still below the
benchmark of 10,000 nesting pairs identified in the recovery plan for
delisting. In addition, productivity, even though variable, is
sufficient to support a growing population.
As a result of continued loss, fragmentation, and
modification of wetland habitats in parts of the wood stork's range, we
find that the continental U.S. wood stork DPS meets the definition of a
threatened species under section 3 of the Act.

Public Comments

We intend that any final action resulting from this proposed rule
will be as accurate and as effective as possible. Therefore, we are
requesting comments from other concerned governmental agencies, Native
American Tribes, the scientific community, industry, or any other
interested party concerning this proposed rule. We particularly seek
information and comments concerning:
(1) The historical and current status and distribution of the wood
stork, its biology and ecology, and ongoing conservation measures for
the species and its habitat.
(2) Wood stork nesting colony location data (latitude/longitude in
decimal degrees to confirm or improve our location accuracy); nest
census counts and survey dates; years when a colony was active or not;
years and dates when a colony was abandoned (fully or partially); and
annual productivity rates (per total nest starts and per successful
nests) and average chicks per nest estimates from continental U.S.
colonies.
(3) Current or planned activities within the geographic range of
the

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continental U.S. breeding population of the wood stork that may impact
or benefit the species, including any acquisition of large tracts of
wetlands, wetland restoration projects, planned developments, roads, or
expansion of agricultural or mining enterprises, especially those near
nesting colonies and surrounding suitable foraging habitats.
Prior to issuing a final rule on this proposed action, we will take
into consideration all comments and additional information we receive.
Such information may lead to a final rule that differs from this
proposal. All comments and recommendations, including names and
addresses, will become part of the administrative record for the final
rule.
You may submit your comments and materials concerning this proposed
rule by one of the methods listed in the ADDRESSES section. If you
submit a comment via http://www.regulations.gov, your entire comment,
including any personal identifying information, will be posted on the
Web site. Please note that comments submitted to this Web site are not
immediately viewable. When you submit a comment, the system receives it
immediately. However, the comment will not be publicly viewable until
we post it, which might not occur until several days after submission.
If you mail or hand deliver hard copy comments that include personal
identifying information, you may request at the top of your documents
that we withhold this information from public review. However, we
cannot guarantee that we will be able to do so. To ensure that the
electronic docket for this rulemaking is complete and all comments we
receive are publicly available, we will post all hard copy comments on
http://www.regulations.gov.

Public Hearing

The Act (16 U.S.C. 1531 et seq.) provides for one or more public
hearings on this proposal, if requested. We must receive your request
for a public hearing within 45 days after the date of this Federal
Register publication (see DATES). Such requests must be made in writing
and addressed to the Field Supervisor (see FOR FURTHER INFORMATION
CONTACT section above).

Background

Much of the basic biological information presented in this section
is based upon existing literature published on the continental U.S.
breeding population of the wood stork. This section summarizes
information found in a large body of published literature and reports,
including the revised recovery plan for the continental U.S. breeding
population of the wood stork (USFWS 1997), The Birds of North America
Online species account for wood stork (Coulter et al. 1999), and the
South Florida Multi-Species Recovery Plan (USFWS 1999).

Taxonomy and Species Description

The wood stork (Mycteria americana) is one of 19 species of storks
that make up the family Ciconiidae (Coulter et al. 1999, p. 3). It is
one of three species of storks found in the western hemisphere (Coulter
et al. 1999, p. 3) and the only stork that breeds north of Mexico
(Ogden 1990, p. B-3). The wood stork shows no obvious morphological
differentiation across its range, and no subspecies have been proposed.
The wood stork is a large, long-legged wading bird, with a head-to-
tail length of 85-115 centimeters (cm) (33-45 inches (in)) and a
wingspread of 150-165 cm (59-65 in- or roughly 5 to 5.5 feet). The
plumage is white, except for iridescent black primary and secondary
wing feathers and a short black tail. Storks fly with their necks and
legs extended. On adults, the rough, scaly skin of the head and neck is
unfeathered and blackish in color, the legs are dark, and the feet are
dull pink. The bill color is also blackish. Immature storks, up to the
age of about 3 years, differ from adults in that their bills are
yellowish or straw-colored and there are varying amounts of dusky
feathers on the head and neck. During courtship and early nesting
season, adults have pale salmon coloring under the wings, fluffy
coverts (feathers under the base of a bird's tail) that are longer than
the tail, and toes that brighten to a vivid pink.

Life Span

Wood storks are considered a long-lived species with delayed
breeding, with first breeding generally occurring for 3- to 4-year old
birds. The greatest recorded longevities are 17+ years for a wild adult
wood stork caught and fitted with a satellite tag and leg bands in
1998, and recently documented at the Harris Neck nesting colony in 2011
(Larry Bryan, SREL, pers. comm., 2011), and 27.5 years for a captive
bird (Brouwer et al. 1992, p. 132).

Feeding

The specialized feeding behavior of the wood stork involves
tactilocation, also called grope feeding, where the stork uses its bill
to find small fish. Wood storks feed primarily on fish between 2 and 25
cm (1 and 10 in) in length (Kahl 1964, pp. 107-108; Ogden et al. 1976,
pp. 325-327). Wood storks also occasionally consume crustaceans,
amphibians, reptiles, mammals, birds, and arthropods (Coulter et al.
1999, p. 7). Wood storks forage in a variety of shallow wetlands,
wherever prey concentrations reach high enough densities, in water that
is shallow and open enough for the birds to be successful in their
hunting efforts (Ogden et al. 1978, pp. 15-17; Browder 1984, p. 94;
Coulter and Bryan 1993, p. 59). Fish populations reach high numbers
during the wet season, but become concentrated in increasingly
restricted habitats as drying occurs. Typical foraging sites include
freshwater marshes, swales, ponds, hardwood and cypress swamps, narrow
tidal creeks or shallow tidal pools, and artificial wetlands (such as
stock ponds; shallow, seasonally flooded, roadside or agricultural
ditches; and impoundments) (Coulter and Bryan 1993, p. 59; Coulter et
al. 1999, p. 5). The wetland foraging areas near a nesting colony play
a vital role during the nesting season (Cox et al. 1994, p. 135).
Nesting wood storks generally use foraging sites that are located
within a 30- to 50-kilometer (km) (18- to 31-mile (mi)) flight range of
the colony; successful colonies are those that have options to feed
during a variety of rainfall and surface water conditions (Coulter
1987, p. 22; Bryan and Coulter 1987, p. 157; Coulter et al. 1999, pp.
17-18; Herring 2007, p. 60; Bryan and Stephens 2007, p. 6; Meyers 2010,
p. 5; Lauritsen et al. 2010, p. 3; Tomlinson 2009, p. 30). Early in the
nesting season, the short-hydroperiod wetlands supply most of the
forage, whereas later, the long-hydroperiod wetlands supply the prey
needed to successfully fledge the offspring (Fleming et al. 1994, p.
754).

Mating and Reproduction

Wood storks are seasonally monogamous, probably forming a new pair
bond every season. There is documented first breeding at 3 and 4 years
old. Nest initiation varies geographically. Wood storks lay eggs as
early as October and as late as June in Florida (Rodgers 1990, pp. 48-
51). Wood storks in north Florida, Georgia, and South Carolina initiate
nesting on a seasonal basis regardless of environmental conditions
(USFWS 1997, p. 6). They lay eggs from March to late May, with fledging
occurring in July and August. Historically, nest initiation in south
Florida was in December and January; however, in response to the
altered habitat conditions (wetland drainage, hydroperiod alteration)
in south Florida, wood storks nesting in Everglades National Park and
in the Big Cypress

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region of Florida have delayed initiation of nesting to February or
March in most years since the 1970s. Colonies that start after January
in south Florida risk having young in the nests when May-June rains
flood marshes and disperse fish, which can cause nest abandonment.
Females generally lay a single clutch of two to five eggs per
breeding season, but the average is three eggs. Females sometimes lay a
second clutch if nest failure occurs early in the season (Coulter et
al. 1999, p. 11). Average clutch size may increase during years of
favorable water levels and food resources. Incubation requires about 30
days and begins after the female lays the first one or two eggs.
Nestlings require about 9 weeks for fledging, but the young return to
the nest for an additional 3 to 4 weeks to be fed. Actual colony
production measurements are difficult to determine because of the
prolonged fledging period, during which time the young return daily to
the colony to be fed.
Wood storks experience considerable variation in production among
colonies, regions, and years in response to local and regional habitat
conditions and food availability (Kahl 1964, p. 115; Ogden et al. 1978,
pp. 10-14; Clark 1978, p. 183; Rodgers and Schwikert 1997, pp. 84-85).
Several recent studies documented production rates to be similar to
rates published between the 1970s and 1990s. Rodgers et al. (2008, p.
25) reported a combined production rate for 21 north- and central-
Florida colonies from 2003 to 2005 of 1.19 0.09 fledglings
per nest attempt (n = 4,855 nests). Rodgers et al. (2009, p. 3) also
reported the St. Johns River basin production rate of 1.49
1.21 fledglings per nest attempt (n = 3,058 nests) and for successful
nests an average fledgling rate of 2.26 0.73 fledglings
per nest attempt (n = 2,105 nests) from 2004 to 2008. Bryan and
Robinette (2008, p. 20) reported rates of 2.3 and 1.6 fledged young per
nesting attempt in 2004 and 2005, respectively, for South Carolina and
Georgia. Murphy and Coker (2008, p. 5) reported that since the wood
stork was listed in 1984, South Carolina colonies averaged 2.08 young
per successful nest with a range of 1.72 to 2.73. The Palm Beach County
(PBC) Solid Waste Authority colony (M. Morrison, PBC, pers. comm.,
2011) was documented with 0.75 fledgling per nesting attempt in 2010,
with annual rates ranging from 0.11 to 1.49 (2003 to 2010). The
Corkscrew Sanctuary colony in Naples, Florida (J. Lauritsen, Audubon,
pers. comm., 2011), documented no nesting in 2010, but an average of
2.29 fledglings per nesting attempt in 2009, with average annual rates
ranging from 0.00 (abandonment) to 2.55 (2001-2010).

Habitat

Wood storks use a wide variety of freshwater and estuarine wetlands
for nesting, feeding, and roosting throughout their range and thus are
dependent upon a mosaic of wetlands for breeding and foraging. For
nesting, wood storks generally select patches of medium to tall trees
as nesting sites, which are located either in standing water such as
swamps, or on islands surrounded by relatively broad expanses of open
water (Ogden 1991, p. 43). Colony sites located in standing water must
remain inundated throughout the nesting cycle to protect against
predation and nest abandonment. A wood stork tends to use the same
colony site over many years, as long as the site remains undisturbed,
and sufficient feeding habitat remains in the surrounding wetlands.
Wood storks may abandon traditional wetland sites if changes in water
management result in water loss from beneath the colony trees.
Typical foraging sites include a mosaic of shallow water wetlands.
Several factors affect the suitability of potential foraging habitat
for wood storks. Foraging habitats must provide both a sufficient
density and biomass of forage fish and other prey and have vegetation
characteristics that allow storks to locate and capture prey. Calm
water, about 5 to 40 cm (2 to 16 in) in depth, and free of dense
aquatic vegetation, is preferred (Coulter and Bryan 1993, p. 61).
During nesting, these areas must also be sufficiently close to the
colony to allow storks to deliver prey to nestlings efficiently.
Hydrologic and environmental characteristics have strong effects on
fish density, and these factors may be some of the most significant in
determining foraging habitat suitability.
Alterations in the quality and amount of foraging habitats in the
Florida Everglades and extensive drainage and land conversions
throughout south Florida led to the initial decline of the wood stork
nesting population. Since listing under the Act, wood stork nesting and
winter counts appear to be increasing slightly in south Florida and the
Everglades (Newman 2009, p. 51; Alvarado and Bass 2009, p. 40), but the
timing and location of nesting has changed in response to alterations
in hydrology and habitat (Ogden 1994, p. 566). The overall distribution
of the breeding population of wood storks is also in transition. The
wood stork appears to have adapted to changes in habitat in south
Florida in part by nesting later, nesting in colonies in the interior
Everglades system (Ogden 1994, p. 566), and by expanding its breeding
range north into Georgia, South Carolina, and North Carolina (Brooks
and Dean 2008, p. 58).

Distribution

The wood stork occurs in South America from northern Argentina,
eastern Peru, and western Ecuador, north into Central America, Mexico,
Cuba, Hispaniola, and the southern United States. The breeding range
includes the southeastern United States in North America, Cuba and
Hispaniola in the Caribbean, and southern Mexico through Central
America (Figure 1). In South America, the breeding range is west of the
Andes south from Colombia to western Ecuador, east of the Andes from
Colombia south through the Amazonas in Brazil to eastern Peru, northern
Bolivia and northern Argentina east to the Atlantic coast through
Paraguay, Uruguay, and north to the Guianas (Figure 1; Coulter et al.
1999, p. 2). The winter range in Central and South America is not well
studied, but wood storks are known to occur year-round as a resident
throughout the breeding range.
At the time of listing in 1984, the range of the continental U.S.
breeding population of wood storks was Florida, Georgia, South
Carolina, and Alabama. Breeding was restricted primarily to peninsular
Florida (22 colonies in 1983), with only four colonies occurring in
Georgia and South Carolina. The current breeding range includes
peninsular Florida (48 colonies in 2010), the coastal plain and large
river systems of Georgia (21 colonies) and South Carolina (13
colonies), and southern North Carolina (1 colony). The breeding range
also extends west to south-central Georgia and the panhandle of Florida
to the Ochlockonee River system. The nonbreeding season range includes
all of Florida; the coastal plains and large river systems of Alabama,
Georgia, South Carolina; and southern North Carolina and eastern
Mississippi.
Wood storks are not true migrants, but some individuals do undergo
lengthy inter-regional travel in response to resource availability
(Coulter et al. 1999, p. 3; Bryan et al. 2008, p. 39). Generally, wood
storks disperse following breeding.

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[GRAPHIC] [TIFF OMITTED] TP26DE12.000

As the rainy season begins in May in south Florida and the
Everglades, post-breeding wood storks, fledglings, and juveniles
disperse throughout peninsular Florida and many move northward along
the coastlines and coastal plain of Georgia, South Carolina, North
Carolina and westward along large river basins in Alabama and eastern
Mississippi. Individuals from northern Florida, Georgia, and South
Carolina colonies also disperse across the coastal plain and coastal
marshes in the southeast United States in July to August after the
breeding season. Most wood storks in this population winter in south
and central Florida and along the coast of peninsular Florida, Georgia,
and South Carolina. These inter-regional movements have been documented
through color marking, banding, radio-telemetry and satellite-telemetry
studies (Comer et al. 1987, p. 165; Ogden 1996, p. 34; Coulter et al.
1999, p. 4; Savage et al. 1999, p. 65; Bryan et al. 2008, pp. 39-41).
Wood storks are seasonal visitors in Texas, Louisiana, the lower
Mississippi Valley, and California. These are post breeders and
juveniles from Central America (Rechnitzer 1956, p. 431; Coulter et al.
1999, pp. 4-5). Bryan et al. (2008, pp. 39-40) suggest that wood storks
observed in western Mississippi and Louisiana originate from Central
America, and wood storks found in eastern Mississippi originate

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from the continental U.S. population. Behaviorally, wood storks are not
predisposed to travel across the open waters like the Gulf of Mexico,
as they use thermals for soaring flight for long-distance movements.
The lack of thermals over open water restricts movements back and forth
across the Gulf of Mexico from Florida to Central and South America or
the Caribbean.

Rangewide Status and Demographics

At the global level, the International Union for Conservation of
Nature (IUCN) classifies the wood stork as a species of ``least
concern.'' This is due to the apparent demographic stability documented
in its large range that encompasses portions of North, Central, and
South America (IUCN 2010, p. 1). Bryan and Borkhataria (2010, p. 2)
compiled and summarized the conservation status for wood storks in
Central and South America and provide the following description with
regard to the rangewide status of the wood stork:

The IUCN Red List/BirdLife International listing classifies the
wood stork as a species of ``least concern'' for its entire range
(BirdLife International 2008, 2009). This classification is based on
breeding/resident range size, population trends, population size.
This classification is due in part to an extremely large global
breeding range (estimated at 14,000,000 km\2\) and a moderately
small to large population estimate (38,000-130,000 birds). Although
the species' global population trend is thought to be decreasing,
the decline is not thought to be sufficiently rapid to reach
critical thresholds to threaten the species (BirdLife 2009: A
``vulnerable'' population exhibits a >30% decline over 10 years or
three generations). Population size estimates for South America
range from 50,000-100,000 wood storks (Byers et al. 1995) and
approximately 48,000-70,000 wood storks in Central and North America
(Kushlan et al. 2002).

The continental U.S. wood stork population decline between 1930 and
1978 is attributed to reduction in the food base necessary to support
breeding colonies, which is thought to have been related to loss of
wetland habitats and changes in hydroperiods (Ogden and Nesbitt 1979,
p. 521; Ogden and Patty 1981, p. 97; USFWS 1997, p. 10; Coulter et al.
1999, p. 18). The continental U.S. breeding population is considered
regionally endangered by IUCN due to habitat degradation (IUCN 2011).
Ogden (1978, p. 143) concluded the continental U.S. wood stork breeding
population in the 1930s was probably less than 100,000 individuals, or
between 15,000 and 20,000 pairs. The estimated continental U.S.
population of breeding wood storks throughout the southeastern United
States declined from 15,000-20,000, to about 10,000 pairs in 1960, to a
low of 2,700-5,700 pairs between 1977 and 1980 (Ogden et al. 1987, p.
752). The low of 2,700 nesting pairs was documented in 1978, during the
severe drought when many wood storks likely did not breed. In the
initial 26-year period of listing under the Act (1984 to 2010), 17
surveys of all known nesting colonies of the wood stork in the
continental U.S. population's breeding range (Florida, Georgia, South
Carolina, and North Carolina) were completed. Eleven of those resulted
in counts exceeding 6,000 pairs. Seven of those higher counts occurred
during the past 10 years (2002, 2003, 2004, 2006, 2008, 2009, and 2010,
Table 1, Service 2010). Two counts of over 10,000 pairs have occurred
during the past 5 years, and the count of 12,720 pairs in 2009 is the
highest on record since the early 1960s. This population estimate along
with a conservative estimate of 4,000 pre-breeding age birds suggest
30,000 storks were inhabiting the United States in 2009 (Bryan and
Borkhataria 2010, p. 2). From 2009 to 2011 there was a decline in
observed wood storks likely due to drought. It should be noted that the
wood stork is a long-lived species that demonstrates considerable
variation in nesting population numbers in response to changing
hydrological conditions. This long reproductive lifespan allows wood
storks to tolerate reproductive failure in some years, and naturally
occurring events have undoubtedly always affected the breeding success
of this species, causing breeding failures and variability in annual
nesting (USFWS 1997, p. 11) and productivity.

Table 1--Wood Stork Nesting Data in the Southeastern United States (Service 2011).
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TOTAL FLORIDA GEORGIA SOUTH CAROLINA NORTH CAROLINA
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YEAR Nesting Nesting Nesting Nesting Nesting
Pairs Colonies Pairs Colonies Pairs Colonies Pairs Colonies Pairs Colonies
--------------------------------------------------------------------------------------------------------------------------------------------------------
1975............................ 9,752 27 9,610 24 142 3 .......... .......... .......... ..........
1976............................ 5,310 17 5,294 16 16 1 .......... .......... .......... ..........
1977............................ 5,263 25 5,125 21 138 4 .......... .......... .......... ..........
1978............................ 2,695 18 2,595 16 100 2 .......... .......... .......... ..........
1979............................ 4,648 24 3,800 22 55 2 .......... .......... .......... ..........
1980............................ 5,063 25 4,766 20 297 5 .......... .......... .......... ..........
1981............................ 4,442 22 4,156 19 275 2 11 1 .......... ..........
1982............................ 3,575 22 3,420 18 135 2 20 1 .......... ..........
1983............................ 5,983 25 5,600 22 363 2 20 1 .......... ..........
1984............................ 6,245 29 5,647 25 576 3 22 1 .......... ..........
1985............................ 5,193 23 4,562 30 557 5 74 1 .......... ..........
1986............................ .......... .......... ** .......... 648 4 120 3 .......... ..........
1987............................ .......... .......... ** .......... 506 5 194 3 .......... ..........
1988............................ .......... .......... ** .......... 311 4 179 3 .......... ..........
1989............................ .......... .......... ** .......... 543 6 376 3 .......... ..........
1990............................ .......... .......... ** .......... 709 10 536 6 .......... ..........
1991............................ 4,073 37 2,440 25 969 9 664 3 .......... ..........
1992............................ .......... .......... ** .......... 1,091 9 475 3 .......... ..........
1993............................ 6,729 43 4,262 29 1,661 11 806 3 .......... ..........
1994............................ 5,768 47 3,588 26 1,468 14 712 7 .......... ..........
1995............................ 7,853 54 5,523 31 1,501 17 829 6 .......... ..........
1996............................ .......... .......... ** .......... 1,480 18 953 7 .......... ..........
1997............................ .......... .......... ** .......... 1,379 15 917 8 .......... ..........
1998............................ .......... .......... ** .......... 1,665 15 1,093 10 .......... ..........
1999............................ 7,768 71 6,109 51 1,139 13 520 8 .......... ..........
2000............................ .......... .......... ** .......... 566 7 1,236 11 .......... ..........
2001............................ 5,582 44 3,246 23 1,162 12 1,174 9 .......... ..........

[[Page 75952]]

2002............................ 7,855 70 5,463 46 1,256 14 1,136 10 .......... ..........
2003............................ 8,813 78 5,804 49 1,653 18 1,356 11 .......... ..........
2004............................ 8,379 93 4,726 63 1,596 17 2,057 13 .......... ..........
2005............................ 5,572 73 2,304 40 1,817 19 1,419 13 32 1
2006............................ 11,279 82 7,216 48 1,928 21 2,010 13 125 1
2007............................ 4,406 55 1,553 25 1,054 15 1,607 14 192 1
2008............................ 6,118 73 1,838 31 2,292 25 1,839 16 149 1
2009............................ 12,720 86 9,428 54 1,676 19 1,482 12 134 1
2010............................ 8,149 94 3,828 51 2,708 28 1,393 14 220 1
2011............................ 9,579 88 5,292 45 2,160 19 2,031 23 96 1
--------------------------------------------------------------------------------------------------------------------------------------------------------
** No survey data available for North and Central Florida.

Previous Federal Action

On February 28, 1984, the Service published a final rule listing
the continental U.S. breeding population of the wood stork as
endangered under the Act, due primarily to the loss of suitable feeding
habitat, particularly in south Florida, and a declining population (49
FR 7332). The endangered status covers wood storks in the States of
Alabama, Florida, Georgia, and South Carolina (the known range of the
continental U.S. breeding population at the time of listing). We
developed a recovery plan in 1986 for the continental U.S. breeding
population of the wood stork. The recovery plan was revised on January
27, 1997, and addressed existing and new threats and species needs.
We published a notice in the Federal Register on November 6, 1991
(56 FR 56882) that we were conducting a 5-year review for all
endangered and threatened species listed before January 1, 1991,
including the wood stork. The notice indicated that if significant data
were available warranting a change in a species' classification, we
would propose a rule to modify the species' status. We did not
recommend a change in the wood stork's listing classification under the
Act at that time. On September 27, 2006 (71 FR 56545), we published a
notice in the Federal Register that we were initiating another 5-year
status review for the wood stork. We solicited information from the
public concerning the status of the species, including the status and
trends of threats to the species under section 4(a)(1) of the Act. We
completed the 5-year status review on September 27, 2007. Completed in
accordance with section 4(c)(2) of the Act, the 5-year status review
contains a detailed description of the species' natural history and
status, including information on distribution and movements, behavior,
population status and trends, and factors contributing to the status of
the continental U.S. breeding population. It also presents a detailed
analysis of the five factors that are the basis for determination of a
species' status under section 4(a)(1) of the Act. A copy of the 5-year
status review is available on our Web site (http://www.fws.gov/ecos/ajax/docs/five_year_review/doc1115.pdf) and includes a recommendation
to reclassify the continental U.S. breeding population of the wood
stork from endangered to threatened.
We received a petition to reclassify the continental U.S. breeding
population of the wood stork as threatened on May 28, 2009, from the
Pacific Legal Foundation on behalf of the Florida Homebuilders
Association. The petition presented the Service's 2007 5-year status
review as its sole supporting information. The petition incorporated
the status review by reference, including a summary of the five-factor
analysis contained in the status review, which included a
recommendation to reclassify the species. We found that the petition
presented substantial information indicating that reclassifying the
continental U.S. breeding population of the wood stork to threatened
may be warranted. We published a notice announcing our 90-day finding
and initiation of the species' status review in the Federal Register on
September 21, 2010 (75 FR 57426).

Current Federal Action

Section 4(b)(3)(B) of the Act requires that for any petition to
revise the Lists of Endangered and Threatened Wildlife and Plants
(Lists) that presents substantial information, we must make a finding
within 12 months of the date of the receipt of the petition, on whether
the requested action is (a) Not warranted, (b) warranted, or (c)
warranted but precluded from immediate proposal by other pending
proposals of higher priority and expeditious progress is being made to
add qualified species to the Lists. This proposed rule constitutes our
12-month finding that the action sought by the May 28, 2009, petition
is warranted.

Distinct Vertebrate Population Segment Analysis

On February 7, 1996, we published in the Federal Register our
``Policy Regarding the Recognition of Distinct Vertebrate Population
Segments Under the Endangered Species Act'' (DPS Policy) (61 FR 4722).
For a population to be listed under the Act as a distinct vertebrate
population segment, three elements are considered: (1) The discreteness
of the population segment in relation to the remainder of the species
to which it belongs; (2) the significance of the population segment to
the species to which it belongs; and (3) the population segment's
conservation status in relation to the Act's standards for listing,
(i.e., is the population segment, when treated as if it were a species,
endangered or threatened). The Act defines ``species'' to include ``* *
* any distinct population segment of any species of vertebrate fish or
wildlife which interbreeds when mature'' (16 U.S.C. 1532(16)). The best
available scientific information supports recognition of the
continental U.S. breeding population of the wood stork as a distinct
vertebrate population segment. We discuss the discreteness and
significance of the population segment within this section; the
remainder of the document discusses the status of the continental U.S.
wood stork DPS.
Discreteness
The DPS policy states that a population segment of a vertebrate
species may be considered discrete if it

[[Page 75953]]

satisfies either one of the following conditions:
(1) It is markedly separated from other populations of the same
taxon as a consequence of physical, physiological, ecological, or
behavioral factors. Quantitative measures of genetic or morphological
discontinuity may provide evidence of this separation; or
(2) It is delimited by international governmental boundaries
between which significant differences exist in control of exploitation,
management of habitat, conservation status, or regulatory mechanisms
that are significant in light of section 4(a)(1)(D) of the Act.
Globally, wood storks occur only in the Western Hemisphere and are
comprised of a mosaic of breeding populations in North, Central, and
South America, and the Caribbean, each with unique nesting sites,
foraging areas, and seasonal movement patterns in response to regional
environmental factors. Historically, wood storks nested in all Atlantic
and Gulf coastal United States from Texas to South Carolina (Bent 1926;
Cone and Hall 1970; Dusi and Dusi 1968; Howell 1932; Oberholser 1938;
Oberholser and Kincaid 1974; Wayne 1910), although the colonies outside
Florida formed irregularly and contained few birds (Ogden and Nesbitt
1979, p. 512).
Currently, the continental U.S. breeding population of wood storks
is documented only in Mississippi, Alabama, Florida, Georgia, South
Carolina, and North Carolina. The continental U.S. wood stork
population represents the northernmost extent of the wood stork's range
and the only population breeding in the continental United States
(USFWS 1997, p. 1; Coulter et al. 1999, pp. 2-3) The continental U.S.
population's breeding range is separated by the Strait of Florida from
the nearest nesting population, which is located in Cuba, 151 km (94
mi); it is approximately 965 km (600 mi) over the Gulf of Mexico from
the nearest North American nesting colony, which breeds in southern
Mexico. However, wood storks are not behaviorally predisposed to travel
across the open ocean. Wood storks use thermals for soaring flight for
long-distance movements. The lack of thermals over water may restrict
movements from Florida to the Caribbean or to Mexico and Central and
South America (Coulter et al. 1999, p. 4). The available evidence does
not suggest that wood storks have crossed the Florida Straits between
the Caribbean islands and the United States or crossed the Gulf of
Mexico to or from Central and South America.
Lengthy inter- and intra-regional movements, related to food
availability, to the wetlands of the Mississippi River Basin and
adjacent coastal plain river basins have been documented from both the
continental U.S. population and Central American wood storks (Coulter
et al. 1999, p. 5; Bryan et al. 2008, pp. 40-41). These studies suggest
post-breeding dispersal occurs along the coastal plain, not across the
Gulf of Mexico, and that wood storks observed in eastern Mississippi
originate from the southeast United States, and those observed in
western Mississippi and Louisiana originate from Central America. A
small percentage of wood storks from both the United States and Central
America apparently overlap during this post-breeding season dispersal
within Mississippi. There may be some small but unknown level of mixing
between continental U.S. and Central American breeding populations in
Mississippi (Bryan et al. 2008, pp. 40-41; R. Borkhataria, University
of Florida, pers. comm., 2010). However, based upon satellite-telemetry
studies (e.g., Hylton 2004; Hylton et al. 2006; Bryan et al. 2008;
Borkahatria 2009; Lauritsen 2010) and other marking studies, mixing
appears negligible. Based on the above information, if the continental
U.S. population were extirpated, it is our assessment that repopulation
from the Central American wood storks would not be sufficient to
replenish the depleted population in the foreseeable future.
Genetic data support the conclusion that wood storks occurring in
the southeastern United States function as one population. Stangle et
al. (1990, p. 15) employed starch gel electrophoretic techniques to
examine genetic variation in Florida wood stork colonies. The study did
not indicate significant allozyme differences within or between
colonies. Van Den Bussche et al. (1999, p. 1083) used a combination of
DNA or allozyme approaches and found low levels of genetic variability
and allelic diversity within Georgia and Florida colonies, suggesting
one population of wood storks in the southeastern United States. A
genetic comparison using mtDNA between continental U.S. and Brazilian
wood storks (the north and south ends of the geographic range) reveals
that either a demographic decline or a recent evolutionary bottleneck
reduced the levels of mitochondrial DNA (mtDNA) variability of the
continental U.S. population (Lopes et al. 2011, p. 1911). The genetic
structuring assessment revealed nonsignificant differentiation between
the continental U.S. and Brazilian wood storks, indicating that either
the populations were only recently separated or that gene flow
continues to occur at low levels, and the haplotype network analysis
indicated low levels of gene flow between populations that were closely
related in the past (Lopes et al. 2011, p. 1911). Genetic studies
indicate that there are nonsignificant differences between continental
U.S. and Brazilian wood storks. However, satellite tracked movements of
U.S. and Central American wood storks indicate that U.S. and Brazilian
birds likely do not interbreed (Hylton 2004; Hylton et al. 2006; Bryan
et al. 2008; Borkahatria 2009; Lauritsen 2010). Based on the genetic
information, we conclude that a past demographic decline has led to the
reduced levels of genetic variability in all populations of wood stork
that were studied, that continental U.S. and other populations were
only recently separated, that the southeastern U.S. populations act as
a single population, and there is negligible or very low gene flow
between populations in the United States and Brazil.
Consequently, we conclude based on the best available information
that the continental U.S. breeding population of the wood stork is
markedly separated from wood stork populations in the Caribbean,
Mexico, Central America, and South America based on physical separation
and wood stork dispersal behavior.
Significance
The DPS policy states that populations that are found to be
discrete will then be examined for their biological or ecological
significance to the taxon to which they belong. This consideration may
include evidence that the loss of the population would create a
significant gap in the range of the taxon. The continental U.S.
breeding population of the wood stork represents the northernmost
portion of the species' range in the world (Coulter et al. 1999, p. 2)
and the only population breeding in the United States. Loss of this
population would result in a significant gap in the extent of the
species' range. Because the nearest populations in the Caribbean and
North America would not likely be able to naturally repopulate the
continental U.S. breeding population if it were extirpated, wood storks
would no longer breed in the Everglades and in the salt and fresh water
wetlands of Florida, Georgia, South Carolina, and North Carolina.
Maintaining a species throughout its historical and current range helps
ensure the species' population viability and reduce impacts to species
as a whole due to localized stochastic

[[Page 75954]]

events. Therefore, we find that loss of continental U.S. breeding
population of the wood stork, whose range has expanded to include
Mississippi and North Carolina (USFWS 2007, p. 11), would constitute a
significant gap in the range of the species as a whole.
Summary
Based on the above analysis, we conclude that the continental U.S.
breeding population of wood storks meets both the discreteness and
significance elements of the 1996 DPS policy. Therefore, we recognize
this population as a valid DPS.

Recovery Actions

We published the original recovery plan for the continental U.S.
breeding population of wood stork on September 9, 1986, and revised it
on January 27, 1997 (Service 1997). The recovery plan identifies four
primary recovery actions for the continental U.S. breeding population
of the wood stork. Species-focused recovery tasks include: (1) Protect
currently occupied habitat, (2) restore and enhance habitat, (3)
conduct applied research necessary to accomplish recovery goals, and
(4) increase public awareness. These primary recovery actions have been
initiated. Many of the actions listed under these categories are of
high priority to implement and are ongoing.
Recovery Task (1): Protect currently occupied habitat. At a
minimum, for continued survival of the continental U.S. breeding
population, currently occupied nesting, roosting, and foraging habitat
must be protected from further loss or degradation. Watersheds
supporting natural nesting habitat should remain unaltered, or be
restored to function as a natural system if previously altered.
Recovery actions under this recovery task include: (1.1) Locate
important habitat, (1.2) prioritize habitat, (1.3) work with private
landowners to protect habitat, (1.4) acquire land, (1.5) protect sites
from disturbance, and (1.6) use existing regulatory mechanisms to
protect habitat.
Recent habitat models (e.g., Gawlik 2002; Herring 2007; Borkhataria
2009; Rodgers et al. 2010); ongoing annual monitoring of nesting
colonies (e.g., Cook and Korboza 2010; Brooks and Dean 2008; Murphy and
Coker 2008; Winn et al. 2008; Frederick and Meyer 2008); surveys of
nesting colony core foraging areas in Florida, Georgia, and South
Carolina (e.g., Herring 2007; Bryan and Stephens 2007; Lauritsen 2010;
Tomlinson 2009; Meyer 2010); and satellite-telemetry studies (e.g.,
Hylton 2004; Hylton et al. 2006; Bryan et al. 2008; Borkahatria 2009;
Lauritsen 2010) are helping to update conservation information and
tools that are used to identify, prioritize, protect, restore, and
acquire important wood stork habitats. Core foraging areas near large
colonies on protected lands, like Corkscrew Swamp Sanctuary in Florida,
Harris Neck National Wildlife Refuge in Georgia, and Washo Plantation
in South Carolina, have been identified. However, alteration and loss
of foraging habitat continues as a threat to recovery, as such habitat
continues to be lost today through the continual expansion of the human
environment, resulting in new development and associated roads and
other infrastructure. The Service has developed a brochure, Wood Stork
Conservation and Management for Land Owners, to assist public and
private land managers in protecting and restoring wood stork habitat
(Service 2001). The wood stork habitat management guidelines are also
being updated (Bryan 2006) and are an important conservation tool to
provide guidance on protecting wood storks and their habitats. In an
effort to minimize loss of wetland habitats important to wood stork
recovery, like those within the core foraging area of a nesting colony,
the Service's South and North Florida Ecological Services Field Offices
have also developed a ``May Affect'' key to assist regulators with
review of wetland dredge and fill permit applications.
Recovery Task (2): Restore and enhance habitat. A prerequisite for
recovery of the wood stork in the southeastern United States is the
restoration and enhancement of suitable habitat throughout the mosaic
of habitat types used by this species. Recovery actions include: (2.1)
Restore the Everglades and Big Cypress system, (2.2) enhance nesting
and roosting sites throughout the range, and (2.3) enhance foraging
habitat by modifying hydrologic regimes in existing artificial
impoundments to maximize use by wood storks.
Wood storks depend upon a mosaic of wetlands throughout the coastal
plain of the southeastern United States for breeding and foraging.
Ecosystems and wetlands are being restored throughout the southeastern
United States through programs such as the Comprehensive Everglades
Restoration Program (CERP) (RECOVER 2009); Kissimmee River Restoration
Project, which includes a goal to restore over 40 square miles of river
and floodplain ecosystem including 43 miles of meandering river channel
and 27,000 acres of wetlands (USACE 2011); and Upper St. Johns Basin
Restoration Project, which has enhanced and restored 150,000 acres of
marsh (SJRWMD 2011). These and other large-scale wetland restoration
projects are significantly contributing to wood stork recovery by
reducing the threat of habitat loss. Management plans such as State
wildlife action plans (http://www.wildlifeactionplans.org/) help to
identify important habitats on which to focus conservation efforts.
Other management plans such as the North American Waterfowl Management
Plan (USFWS 2011) also help to identify focus areas for conservation.
By highlighting important habitats or areas, such as the ACE Basin and
Winyah Bay in South Carolina, funds and conservation initiatives are
directed towards restoring these important habitat areas and contribute
to recovery by reducing the threat due to loss of habitat. Thousands of
acres are being protected, enhanced, restored, and brought under
conservation easements to assist in wildlife conservation through
programs such as the Wetland Reserve Program (WRP) and the Farm Bill,
including 70,000 acres of wetlands in Alabama, Florida, Georgia,
Mississippi, North Carolina, and South Carolina in 2010 (NRCS 2011).
The WRP is a voluntary program offering landowners the opportunity to
protect, restore, and enhance wetlands on their property. The U.S.
Department of Agriculture, Natural Resources Conservation Service
(NRCS) provides technical and financial support to help landowners with
their wetland restoration efforts. The goal of the NRCS is to achieve
the greatest wetland functions and values, along with optimum wildlife
habitat, on every acre enrolled in the program. This program offers
landowners an opportunity to establish long-term conservation and
wildlife practices and protection, and therefore provides some benefits
to wood stork recovery. In Florida, the WRP program has restored over
200,000 acres of wetlands (Simpkins, Service, pers. comm., 2011) and
over 115,000 acres in Alabama, Georgia, and South Carolina. A majority
of the Florida WRP-restored acres have been within the Everglades and
Big Cypress systems. A 2006 WRP restoration of 200 acres of farmland in
Camilla, Georgia, now supports the newest Georgia wood stork colony,
with over 100 nesting pairs annually. This task will be complete once
viable nesting occurs throughout the range of this DPS. The most
significant wetland restoration goal for wood storks is to recover
viable nesting subpopulations in the traditional Everglades and Big
Cypress nesting areas as outlined by CERP. Overall,

[[Page 75955]]

future wetland restoration efforts in the Southeast U.S. will be
beneficial to wood stork recovery.
Recovery Task (3): Conduct applied research necessary to accomplish
recovery goals. Recovery efforts for the wood stork will be more
effective with a better understanding of population biology, movement
patterns of continental U.S. and neighboring populations of wood
storks, foraging ecology and behavior, the importance of roost sites,
and the possible impacts of contaminants. Recovery actions include:
(3.1) Determine movement patterns of continental U.S. and neighboring
populations of wood storks, (3.2) determine population genetics, (3.3)
monitor productivity of stork populations, (3.4) monitor survivorship
of stork populations, (3.5) determine extent of competition/cooperation
between wood storks and other wading birds in mixed nesting colonies,
(3.6) determine foraging ecology and behavior, (3.7) determine the
importance of roost sites, and (3.8) determine the impacts of
contaminants on wood stork populations. The following is a summary of
several recent monitoring and research findings.
The South Florida Wading Bird Report (1996-2010) annually reports
on habitat monitoring and research with respect to the CERP and
foraging and nest monitoring projects for wood storks and wading birds
utilizing the Everglades and Big Cypress systems. This report provides
an annual assessment on the Restoration Coordination and Verification
Program (RECOVER), the system-wide science arm of the CERP. Per
Recovery Action 3.1 and 3.6, satellite-telemetry studies are providing
new insight into movement patterns (e.g., Hylton 2004; Bryan et al.
2008; Borkhataria 2009; Lauritsen 2010). Surveys to determine foraging
distances from nesting colonies and satellite-telemetry research are
helping to update our understanding of wood stork foraging ecology and
of core foraging areas (e.g., Herring 2007; Bryan and Stephens 2007;
Borkhataria 2009; Meyers 2010; Lauritsen 2010; Tomlinson 2009).
Satellite-telemetry data and banding studies are helping to refine
survival estimates (Borkhataria 2009, pp. 63-64) for population
modeling (Borkhataria 2009) as identified under Recovery Action 3.4.
Ongoing systematic reconnaissance flights of the Everglades, Kissimmee
River, water conservation areas, Big Cypress National Preserve, and
Upper St. Johns River are monitoring wood stork abundance and
distribution in south Florida (Cheek 2010, pp. 22-26; Alvarado and Bass
2010, pp. 30-39; Nelson 2010, p. 40; D. Hall, SJRWMD, pers. comm.,
2008). Annual nesting colony surveys help to monitor the status of the
breeding population. Per Recovery Action 3.3, recent productivity
research and monitoring efforts have documented productivity rates to
be similar to rates documented between the 1970s and 1990s (Rodgers et
al. 2008; Bryan and Robinette 2008), and Rodgers et al. (2008, p. 25)
suggest the need to develop an unbiased estimator of productivity that
takes into consideration the lack of nesting during some years to more
accurately estimate wood stork productivity at the regional level. A
genetic structuring and haplotype network analysis comparison indicates
that either a demographic decline or a recent evolutionary bottleneck
reduced the levels of genetic variability in the continental U.S.
population (Lopes et al. 2011, p. 1911) is research addressing Recovery
action 3.2. The genetic structuring assessment revealed nonsignificant
differentiation, indicating that continental U.S. and Brazilian wood
stork populations were only recently separated or that gene flow
between these populations continues to occur at low levels. The
haplotype network analysis indicated low current levels of gene flow
between populations that were closely related in the past (Lopes et al.
2011, p. 1911).
Recovery Task (4): Increase public awareness. Wood storks utilize a
wide variety of wetland habitats. They are visually unique and generate
interest from the public. These factors have made the wood stork the
subject of many environmental education materials and programs. There
are many brochures, videos, and educational packets available. Recovery
actions include: (4.1) Increase awareness and appreciation through
educational materials, and (4.2) provide opportunities for the public
to view wood storks in captivity.
Examples of such wood stork educational efforts to increase public
awareness can be found on our Web site (http://www.fws.gov/northflorida/WoodStorks/wood-storks.htm) and the Web sites of many of
our recovery partners, including the Everglades National Park (http://www.nps.gov/ever/naturescience/woodstork.htm), Florida Fish and
Wildlife Conservation Commission (http://myfwc.com/research/wildlife/birds/wood-storks/), Georgia Department of Natural Resources (http://www.georgiawildlife.com/sites/default/files/uploads/wildlife/nongame/pdf/accounts/birds/mycteria_americana.pdf), South Carolina Department
of Natural Resources (http://www.dnr.sc.gov/cwcs/pdf/Woodstork.pdf),
University of Florida (http://www.wec.ufl.edu/faculty/frederickp/woodstork/), Audubon Society (http://birds.audubon.org/species/woosto),
Corkscrew Sanctuary Swamp (http://www.corkscrewsanctuary.org/Wildlife/Birds/profiles/wost.pdf), and others.
Opportunities for the public to view wood storks in the wild
include almost all National Wildlife Refuges (NWR) and National Parks
and Preserves in Florida and coastal Georgia and South Carolina,
including the Everglades National Park, Ten Thousand Island NWR, J.N.
Ding Darling NWR, Loxahatchee NWR, Pelican Island NWR, Merritt Island
NWR, Harris Neck NWR, and ACE Basin NWR. Several wood stork nesting
colonies can also be seen at public observation areas that do not
disturb the colony, such as Audubon's Corkscrew Swamp Sanctuary,
Parotis Pond in Everglades National Park, Pelican Island NWR, St.
Augustine Alligator Farm, Jacksonville Zoo and Gardens, and Harris Neck
NWR.

Recovery Achieved

The recovery criteria for the continental U.S. breeding population
DPS of wood storks state that reclassification from endangered to
threatened could be considered when there are 6,000 nesting pairs and
annual average regional productivity is greater than 1.5 chicks per
nest per year (both calculated over a 3-year average). Although
variable, productivity appears to be sufficient to support continued
population growth as evidenced by the increasing nesting population and
range expansion.
1. Nesting pairs. The continental U.S. breeding population of the
wood stork has been increasing since it was listed in 1984 (Brooks and
Dean 2008, p. 58; Borkhataria 2009, p. 34). Regional nesting surveys to
census wood stork colonies have been continuous in south Florida and
Georgia since 1976, and in South Carolina since 1981. Nest censuses of
the entire breeding range were conducted in 1975-1986, 1991, 1993-1995,
1997, 1999, and 2001-2010 (Table 1). The 3-year average for nesting
pairs has exceeded the reclassification criterion of 6,000 every year
since 2003 (Table 2). However, the nesting pair average is well below
the 5-year average of 10,000 nesting pairs (a benchmark for delisting),
and the 5-year averages for nesting in the Everglades and Big Cypress
Systems are below 2,500 nesting pairs (another benchmark for
delisting), as nesting in south Florida remains variable (Table 2).

[[Page 75956]]

Table 2--Wood Stork Nesting Data in the Southeastern United States and 3-year Averages (Service 2011).
--------------------------------------------------------------------------------------------------------------------------------------------------------
Total South FL Central/North FL GA SC NC
-------------------------------------------------------------------------------------------------------------
Year Nesting Nesting Nesting Nesting Nesting Nesting
pairs 3yr Avg pairs 3yr Avg pairs 3yr Avg pairs 3yr Avg Pairs 3yr Avg pairs 3yr Avg
--------------------------------------------------------------------------------------------------------------------------------------------------------
1981...................................... 4,442 ....... 2,428 ....... 1,728 ....... 275 ....... 11 ....... ....... .......
1982...................................... 3,575 ....... 1,237 ....... 2,183 ....... 135 ....... 20 ....... ....... .......
1983...................................... 5,983 4,667 2,858 2,174 2,742 2,218 363 258 20 17 ....... .......
1984...................................... 6,245 5,268 1,245 1,780 4,402 3,109 576 358 22 21 ....... .......
1985...................................... 5,193 5,807 798 1,634 3,764 3,636 557 499 74 39 ....... .......
1986...................................... ......... ....... 643 895 ....... ....... 648 584 120 72 ....... .......
1987...................................... ......... ....... 100 514 ....... ....... 506 570 194 129 ....... .......
1988...................................... ......... ....... 755 499 ....... ....... 311 488 179 164 ....... .......
1989...................................... ......... ....... 515 457 ....... ....... 543 453 376 250 ....... .......
1990...................................... ......... ....... 475 582 ....... ....... 709 521 536 364 ....... .......
1991...................................... 4,073 ....... 550 513 1,890 ....... 969 740 664 525 ....... .......
1992...................................... ......... ....... 1,917 981 ....... ....... 1,091 923 475 558 ....... .......
1993...................................... 6,729 ....... 587 1,018 3,675 ....... 1,661 1,240 806 648 ....... .......
1994...................................... 5,768 ....... 741 1,082 2,847 ....... 1,468 1,407 712 664 ....... .......
1995...................................... 7,853 6,783 1140 823 4,383 3,635 1,501 1,543 829 782 ....... .......
1996...................................... ......... ....... 1215 1,032 ....... ....... 1,480 1,483 953 831 ....... .......
1997...................................... ......... ....... 445 933 ....... ....... 1,379 1,453 917 900 ....... .......
1998...................................... ......... ....... 478 713 ....... ....... 1,665 1,508 1,093 988 ....... .......
1999...................................... ......... ....... 2,674 1,190 ....... ....... 1,139 1,394 520 843 ....... .......
2000...................................... ......... ....... 3,996 2,383 ....... ....... 566 1,123 1,236 950 ....... .......
2001...................................... 5,582 ....... 2,888 3,186 358 ....... 1,162 956 1,174 977 ....... .......
2002...................................... 7,855 ....... 3,463 3,449 2,000 ....... 1,256 995 1,136 1,182 ....... .......
2003...................................... 8,813 7,417 1,747 2,699 4,057 2,138 1,653 1,357 1,356 1,222 ....... .......
2004...................................... 8,379 8,349 1,485 2,232 3,241 3,099 1,596 1,502 2,057 1,516 ....... .......
2005...................................... 5,572 7,588 591 1,274 1,713 3,004 1,817 1,689 1,419 1,611 32 .......
2006...................................... 11,279 8,410 2,648 1,575 4,568 3,174 1,928 1,780 2,010 1,829 125 .......
2007...................................... 4,406 7,086 696 1,312 857 2,379 1,054 1,600 1,607 1,679 192 116
2008...................................... 6,118 7,268 344 1,229 1,494 2,306 2,292 1,758 1,839 1,819 149 155
2009...................................... 12,720 7,748 5,816 2,285 3,612 1,988 1,676 1,674 1,482 1,643 134 158
2010...................................... 8,141 8,993 1,220 2,460 2,600 2,571 2,708 2,225 1,393 1,571 220 168
2011...................................... 9,579 10,147 2,131 3,056 3,161 3,124 2,160 2,181 2,031 1,635 96 141
--------------------------------------------------------------------------------------------------------------------------------------------------------

2. Productivity. There is also a need to systematically determine
reproductive success (number of fledged young per nest and number of
fledged young per successful nest) for a majority of the colonies in
the same year(s) to better estimate productivity of the breeding
population (USFWS 1997, p. 24). The Service acknowledges that the
productivity dataset is incomplete, with less than 25 percent of the
colonies surveyed for productivity during the past 4 years and 50
percent surveyed between 2003 and 2007. Brooks and Dean (2008, p. 56)
indicate the average productivity rate for all colonies monitored in
the southeastern United States was 1.5 chick/nest attempt between 2004
and 2006; 1.2 chick/nest attempt between 2003 and 2005; and 1.5 chick/
nest attempt between 2003 and 2006 (Brooks and Dean 2008, p. 56).
Rodgers et al. (2008, p. 25) found that colonies farther north in
Florida exhibited greater productivity, and that colonies in
northeastern and northwestern Florida had greater fledging rates than
colonies farther south in central Florida. Bryan and Robinette (2008,
p. 20) found Georgia and South Carolina rates similar to North Florida
rates. Due to funding and manpower constraints, rangewide, Statewide,
and regional monitoring of wood stork productivity only has occurred
episodically (e.g., early 1980s and 2000s). As there are now over 80
wood stork colonies, Rodgers et al. (2008, p. 32) identifies the need
to develop a long-term program of monitoring that relies on monitoring
of fewer colonies.
Based upon the nesting population criteria in the recovery plan, we
can consider the continental U.S. breeding population of the wood stork
for reclassification to threatened status at this time because wood
storks and their habitat would continue to receive the protections of
the Act, and management efforts continue to maintain, enhance, and
restore the amount and quality of available habitat to support a
growing population. For the following reasons, we believe that the
continental U.S. breeding population of the wood stork has surpassed
the recovery criteria outlined as necessary for reclassification. As
shown in Table 2 of this document, the nesting population is increasing
and well above the reclassification benchmark (Brooks and Dean 2008, p.
58; Table 2). The total number of nesting colonies has remained stable
in south Florida and the number of colonies in central and north
Florida, Georgia, South Carolina, and North Carolina continue to
increase (Ogden et al. 1987, p. 754; Brooks and Dean 2008, p. 54; Table
1). The nesting range continues to expand with new colonies documented
in North Carolina and western Georgia. Although variable (particularly
in south Florida) and not yet well documented, productivity appears to
be sufficient to support continued population growth, as evidenced by
the increasing population and range expansion described above.
Population trends suggest that the overall population may approach the
delisting benchmark of 10,000 nesting pairs during the next 15 to 20
years. Nesting numbers suggest a stable or increasing population,
however, data are not available to evaluate the productivity criterion
of 1.5 chicks per nest per year.

Summary of Factors Affecting the Species

Section 4 of the Act and its implementing regulations (50 CFR part
424) set forth the procedures for listing, reclassifying, or removing a
species from, the Federal Lists of Endangered

[[Page 75957]]

and Threatened Wildlife and Plants. Under section 3 of the Act, a
species is ``endangered'' if it is in danger of extinction throughout
all or a ``significant portion of its range'' and is ``threatened'' if
it is likely to become endangered within the foreseeable future
throughout all or a ``significant portion of its range.'' The word
``range'' refers to the range in which the species currently exists,
and the word ``significant'' refers to the value of that portion of the
range being considered to the conservation of the species. The
``foreseeable future'' is the period of time over which events or
effects reasonably can or should be anticipated, or trends
extrapolated. A species may be 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.
The following analysis examines all five factors currently
affecting or that are likely to affect the wood stork within the
foreseeable future:

A. The Present or Threatened Destruction, Modification, or Curtailment
of Its Habitat or Range

Throughout its range in the southeastern United States, wood storks
are dependent upon wetlands for breeding and foraging. Preventing loss
of wood stork nesting habitat and foraging wetlands within a colony's
core foraging area is of the highest priority. In addition, winter
foraging habitat is important to recovery, as it may determine the
carrying capacity of the continental U.S. wood stork DPS. While the
immediacy and the magnitude of this factor are substantially reduced
when compared to when this species was originally listed, the
destruction, fragmentation, and modification of its wetland habitats
continues to occur and could accelerate in the absence of the
protections of the Act.
Hefner et al. (1994, p. 21) estimated that 1.3 million acres of
wetlands lost in the southeastern United States between the mid 1970s
and mid 1980s were located in the Gulf-Atlantic Lower Coastal Plain, an
area upon which wood storks are dependent. Ceilley and Bartone (2000,
p. 70) suggest that short hydroperiod wetlands provide a more important
pre-nesting food source and provide for a greater early nestling
survivorship for wood storks than previously known. Wetlands that wood
storks use for foraging are being lost through permitted activities
where mitigation is provided. However, it is not known if wood stork
foraging wetlands are being replaced with like-quality foraging
wetlands within the core foraging area of an impacted colony. Lauritsen
(2010, pp. 4-5) suggests that today's mitigation practices lead to a
disproportionate loss of short hydroperiod wetlands. The impacts of the
loss of short hydroperiod (isolated) wetlands, which supply most of the
food energy for initiating reproduction (Fleming et al. 1994, p. 754),
may result in abandonment of nest colonies by wood storks (e.g.,
Corkscrew Swamp Sanctuary). Frederick and Meyer (2008, p. 15) suggest
that the decline in colony size in Florida reflects the increasingly
fragmented nature of Florida's wetlands resulting from development.
The decline of south Florida's Everglades and Big Cypress
ecosystems is well-documented (e.g., Davis and Ogden 1994). Prior to
1970, a majority (70 percent) of the wood stork population nested south
of Lake Okeechobee and declined from 8,500 nesting pairs in the early
1960s to around 500 pairs in the late 1980s and early 1990s (Service
1997). The primary cause of this decline was the loss of wetland
function of these south Florida ecosystems that resulted in reduced
prey availability or loss of wetland habitats (Service 1997, p. 10).
Wood storks use manmade wetlands for foraging and breeding
purposes. Manmade wetlands include, but are not limited to, storm water
treatment areas and ponds, golf course ponds, borrow pits, reservoirs,
roadside ditches, agricultural ditches, drainages, flow-ways, mining
and mine reclamation areas, and dredge spoil sites. The impacts can be
positive in certain scenarios as these wetlands can provide protected
foraging and nesting habitat, and may offset some losses of natural
wetlands caused by development. A significant number of wood stork
colonies are located where water management practices can impact the
nesting habitat negatively. Colonies that are perpetually flooded will
have no tree regeneration. Draining surface waters of a colony's
wetland or pond will prevent wood storks from nesting, and lowered
water levels after nest initiation facilitate raccoon predation.
Lowering surface water or water table may occur through water control
structures, manipulating adjacent wetlands, or water withdrawals from
the local aquifer and can prevent wood storks from nesting or cause
colony failure.
While habitat loss, fragmentation, and degradation continue to
occur throughout the range of the continental U.S. population of wood
stork, there are also protection, acquisition, and restoration efforts
in progress. Natural wetlands are being targeted for acquisition to be
protected through the management of public lands for wildlife and water
conservation (NRCS 2006, p. 1). In Florida, the Wetlands Reserve
Program has restored over 200,000 acres of wetlands and over 115,000
acres in Alabama, Georgia, and South Carolina during the past 18 years.
Thousands of acres of wetlands are also being protected on private
lands to assist in habitat and wildlife protection through restoration
in conjunction with establishing conservation easements (Dahl 2006, p.
16). Wetland losses are being avoided, minimized, and mitigated through
the regulatory process (Votteler and Muir 2002, pp. 1-2). Large-scale
restoration projects like the CERP, Kissimmee River Restoration
Project, and St. Johns River Headwaters Restoration Project are
significant conservation efforts that greatly benefit wood stork
recovery.
Additionally, the species' response to the threat of habitat loss
and degradation indicates its ability to adapt and seek out new nesting
and foraging areas. Since 1980, wood storks have expanded their
breeding range north into Georgia, South Carolina, and North Carolina,
and the total number of breeding adults is now approaching the
delisting criterion set out in the species' recovery plan. Seventy
percent of the population now breeds north of Lake Okeechobee and the
Everglades (Brooks and Dean 2008, p. 53). These positive indicators
throughout the range suggest that the viability of the continental U.S.
wood stork DPS may no longer be as closely tied to the health of the
Everglades for reproduction.
With regard to important wood stork habitats, a number of the
nesting colonies occur on Federal conservation lands and are
consequently afforded protection from development and large-scale
habitat disturbance. Wood stork colonies also occur on a variety of
State-owned properties, and existing State and Federal regulations
provide protection on these sites. However, approximately half of known
wood stork colonies occur on private lands. Through conservation
partnerships, colonies can be protected through the owners'
stewardship. In an effort to minimize potential loss of colony sites,
partnerships have been developed through conservation easements,

[[Page 75958]]

wetland restoration projects, and other conservation means. Also, the
wetland areas near nesting colonies play a vital role in the success of
a nesting colony. Due to the regulatory status of wetlands,
conservation of wetlands shown to be important to wood storks can be
largely achieved through the application of existing wetland laws, such
as the Clean Water Act (33 U.S.C. 1251 et seq.) and the interagency
cooperation provisions of the Act.
In summary, loss, fragmentation, and modification of wetland
habitats continue as threats to wood storks. Changes in local habitat
conditions are known to impact wood storks. Based on the best available
scientific information, it is our assessment that the species is
showing the ability to respond to these threats through expansion of
its range, adjusting reproductive timing, and utilizing a variety of
wetlands for foraging, roosting, and breeding, including manmade
wetlands. Historically, the core of the wood stork breeding population
was located in the Everglades and Big Cypress systems of south Florida.
Populations there had diminished because of deterioration of the
habitat. In recognition of the importance of the Everglades and Big
Cypress systems to wood stork recovery, the recovery plan stated that,
as a prerequisite for full recovery, these ecosystems should once again
provide the food resources that are necessary to support traditional
wood stork nesting patterns at historical nesting areas. However,
current data show that the breeding range has now almost doubled in
area and shifted northward along the Atlantic coast as far as
southeastern North Carolina. As a result of their range expansion,
dependence of wood storks on any specific wetland complex has been
reduced. Even though habitat destruction and modification are still a
threat to recovery, the improved wood stork population statistics
suggest that wetland habitat is not yet limiting the population, at
least at the landscape level (USFWS 2007, p. 16). Habitat loss,
fragmentation, and modification of wetland habitats continue around
nesting colonies and core foraging areas, and are a significant factor
affecting the viability of the continental U.S. wood stork DPS.

B. Overutilization for Commercial, Recreational, Scientific, or
Educational Purposes

Monitoring of and research on wood storks over the past 20 years
has increased. A small number of scientific research permits with
potential to harm individual wood storks have been issued. This level
of take/harm is not expected to adversely impact wood stork recovery or
present a threat to the species.
Wading birds and other waterbird species, including wood storks,
can impact production at fish farms. A Georgia catfish farmer located
approximately 25 miles west of the Chewmill and Birdsville colonies in
Jenkins County, Georgia, has documented hundreds of woods storks
aggregating and foraging on the littoral edges of the ponds during the
late summer in recent years. U.S. Department of Agriculture, Wildlife
Services Division (Wildlife Services) has documented hundreds of wood
storks, and in one case 1,000 wood storks, roosting on fish pond dikes
in the eastern Mississippi, west-central Alabama area (J. Taylor, U.S.
Department of Agriculture, pers. comm., 2007). Wildlife Services found
that the wood storks were generally loafing, and if they were feeding,
they were taking diseased and oxygen-deprived fish and not impacting
production. Nonetheless, operators of fish farms often respond to such
activities by taking wood storks. Unpermitted wood stork take has been
documented at a Mississippi catfish farm and a Florida tropical fish
farm. Each of these incidents ended in prosecution for shooting wood
storks. However, wood stork take at aquaculture facilities likely still
occurs. To what extent this type of take occurs is unknown. Migratory
Bird Treaty Act (MBTA; 16 U.S.C. 701 et seq.) depredation permits
assist in minimizing unauthorized take. Depredation permits are issued
to allow the take of migratory birds that are causing serious damage to
public or private property, pose a health or safety hazard, or are
damaging agricultural crops or wildlife. Wildlife Services provides
expert technical advice and information regarding hazing and harassment
techniques.
Research permits are issued to eliminate or minimize impacts to
wood storks from scientific research. Overutilization was not
identified as a threat at the time of listing in 1984, and we conclude
that overutilization for commercial, recreational, scientific, or
educational purposes is not a threat to the continental U.S. wood stork
DPS now or in the foreseeable future.

C. Disease or Predation

There is limited information regarding potential impacts from
disease or parasites. Hematozoa (blood parasites) have been documented
to a limited extent in wood storks in Florida and Georgia (Forrester et
al. 1977, p. 1273; Fedynich et al. 1998, p. 166). Avian malaria has
recently been documented in continental U.S. wood storks, but the
available information does not indicate that avian malaria is a
significant factor affecting the DPS.
Adequate water levels under nesting trees or surrounding nesting
islands deter raccoon predation of wood stork colonies. Water level
manipulation that keeps levels too low can facilitate raccoon predation
of wood stork nests. In many cases, colonies also have a population of
alligators nearby that deter raccoon predation (Coulter and Bryan 1995,
p. 242), and removal of alligators from a nesting colony site could
lead to increased raccoon predation. Human disturbance may cause adults
to leave nests, exposing the eggs and downy nestlings to predators
(e.g., fish crows), sun, and rain. Great horned owls have been
documented nesting in and near colonies and likely impact the colony to
some degree.
A breeding population of Burmese pythons has been documented in the
Florida Everglades, and a recent study documented that pythons had
preyed upon wood storks (Dove et al. 2011, p. 128). If these snakes or
other species of nonnative reptiles become established in additional
areas within the south Florida ecosystem, they could pose a threat to
nesting wood storks and other species of colonial-nesting water birds
but at the present time pythons do not pose a significant factor
affecting the continental U.S. breeding population of wood stork.
As summarized above, we have a few documented instances of disease
and predation within range of the continental U.S. wood stork DPS.
However, this information does not indicate that disease or predation
occur at a level that would threaten the continental U.S. wood stork
DPS, now or in the foreseeable future. We will continue to work closely
with our State and Federal wildlife agency partners, those who monitor
wildlife diseases in the wild, and those conducting research of wood
storks in order to monitor these potential threats.

D. The Inadequacy of Existing Regulatory Mechanisms

In addition to the Act, the MBTA provides Federal protection to the
continental U.S. wood stork DPS. Florida, Georgia, South Carolina,
North Carolina, Alabama, and Mississippi wildlife laws also list and
protect wood storks. These Federal and State laws prohibit the taking
of a wood stork, their nests, or their eggs, except as authorized
through permitted activities such as scientific research and
depredation permits. However, the MBTA and State

[[Page 75959]]

laws do not prohibit clearing, alteration, or conversion of wetland
foraging habitats or nesting colony sites during the non-nesting
season.
The Clean Water Act (CWA) regulates dredge and fill activities that
would adversely affect wetlands, which constitute wood stork habitat.
Section 404 of the CWA regulates the discharge of dredged or fill
materials into wetlands. Discharges of dredged or fill materials are
commonly associated with projects to create dry land for development
sites, water-control projects, and land clearing. The U.S. Army Corps
of Engineers (Corps) and the Environmental Protection Agency (EPA)
share the responsibility for implementing the permitting program under
section 404 of the CWA. These federal actions must not jeopardize the
continued existence of any species protected under the Act.
When impacts to wetlands cannot be avoided or minimized, wetland
mitigation is often employed to replace an existing wetland or its
functions by creating a new wetland, restoring a former wetland, or
enhancing or preserving an existing wetland. This is done to compensate
for the authorized destruction of the existing wetland. As discussed
earlier, it is not known if wood stork foraging wetlands are being
replaced with like-quality foraging wetlands within the core foraging
areas of impacted colonies.
There is currently little protection for isolated wetland habitats
under section 404 of the CWA. A 2001 U.S. Supreme Court opinion (Solid
Waste Agency of Northern Cook County (SWANCC) v. US Army Corps of
Engineers, 531 U.S. 159 (2001)) substantially reduced the jurisdiction
of the Federal Government in regulating isolated wetlands. While many
States in the southeastern United States regulate those activities
affecting wetlands that are not protected by section 404 of the CWA,
Florida is the only State known to regulate isolated wetlands. In South
Carolina, Georgia, Alabama, and North Carolina, there are no State laws
that protect isolated wetlands. The EPA and the Corps have developed
draft guidance for determining whether a waterway, water body, or
wetland is protected by the CWA (76 FR 24479, May 2, 2011). If
implemented, the guidance will increase the extent of waters over which
the agencies assert jurisdiction under the CWA and thus would provide
protection to additional wood stork foraging wetlands that are
currently unprotected from modification or elimination.
The Service recommends, through its Wood Stork Habitat Management
Guidelines (Ogden 1990), that active colony sites be protected from
local hydrologic changes and from human activities (e.g. timber
harvesting, vegetation removal, construction, and other habitat-
altering activities) which are likely to be detrimental to the colony
(Service 1997, p. 18). The Service also recommends that feeding sites
be protected to the maximum extent possible. The Service's South
Florida and Jacksonville Ecological Services Field Offices have
developed ``May Affect'' keys to assist regulators with review of
wetland dredge and fill permit applications and in an effort to
minimize loss of wetland habitats important to wood stork recovery,
like those within the core foraging area of a nesting colony.
In summary, there are a number of regulatory mechanisms implemented
by Federal and State agencies to protect wood storks and conserve their
habitat. Take of wood storks is illegal under both the Act and MBTA.
The CWA minimizes impacts on jurisdictional wetlands that are important
to Wood Storks, however the CWA alone is not sufficient to eliminate
all impacts, as discussed in Factor A. Whether existing habitat
protections and conservation mechanisms are inadequate can only be
assessed by monitoring the status of the wood stork population. Recent
trends indicate that the range is expanding and the breeding population
has increased, suggesting that the combination of the CWA, the Act,
MBTA, and state regulations are adequate to protect jurisdictional
wetlands to allow population growth. However, non-jurisdictional
wetlands continue to be lost to development due to lack of existing
regulatory mechanisms, and therefore, loss of these wetlands continues
as a threat to this species.

E. Other Natural or Manmade Factors Affecting Its Continued Existence

Climate Change
The terms ``climate'' and ``climate change'' are defined by the
Intergovernmental Panel on Climate Change (IPCC). ``Climate'' refers to
the mean and variability of different types of weather conditions over
time, with 30 years being a typical period for such measurements,
although shorter or longer periods also may be used (IPCC 2007, p. 78).
The term ``climate change'' thus refers to a change in the mean or
variability of one or more measures of climate (e.g., temperature or
precipitation) that persists for an extended period, typically decades
or longer, whether the change is due to natural variability, human
activity, or both (IPCC 2007, p. 78). Various types of changes in
climate can have direct or indirect effects on species. These effects
may be positive, neutral, or negative, and they may change over time,
depending on the species and other relevant considerations, such as the
effects of interactions of climate with other variables (e.g., habitat
fragmentation) (IPCC 2007, pp. 8-14, 18-19). In our analyses, we use
our expert judgment to weigh relevant information, including
uncertainty, in our consideration of various aspects of climate change.
The IPCC concluded that evidence of warming of the climate system
is unequivocal (IPCC 2007a, p. 30). Numerous long-term changes have
been observed, including changes in arctic temperatures and ice,
widespread changes in precipitation amounts, ocean salinity, wind
patterns, and aspects of extreme weather, including droughts, heavy
precipitation, heat waves, and the intensity of tropical cyclones (IPCC
2007b, p. 7). While continued change is certain, the magnitude and rate
of change is unknown in many cases. Species that are dependent on
specialized habitat types, are limited in distribution, or are located
in the extreme periphery of their range will be most susceptible to the
impacts of climate change. Such species would currently be found at
high elevations or in extreme northern/southern latitudes, or are
dependent on delicate ecological interactions or sensitive to nonnative
competitors. Wood storks nest in a wide variety of natural and human
made habitats (e.g., fresh water wetlands to estuarine environs,
cypress strands to mangrove islands, lake edges to river edges,
impoundments to borrow pits); they are not dependent upon specialized
habitat. They nest in trees and shrubby vegetation (native to exotic)
where water is surrounding (island) or water is underneath the nesting
vegetation and where there is suitable foraging habitat nearby (shallow
water wetlands). The marshes and wetlands they use may be impacted by
climate change depending on their location but wood storks have been
shown to find other habitat if existing locations become unavailable.
Information on the subject of climate change in our files is not
specific to the wood stork. While predictions of increased drought
frequency, intensity, and duration suggest that nestling survival could
be a limiting factor for the wood stork due to increased predation or
possible loss or shift in the location of coastal colonies due to sea
level rise, the species possesses other biological traits, like
adaptability to

[[Page 75960]]

changing habitat conditions that provide resilience to this threat.
Wood storks are already responding to habitat changes by altering their
nest locations. This has been seen in the recent expansion from
Everglades colony locations in Florida to other areas in the
southeastern United States (Brooks and Dean 2008). These expansions are
in response to annual cycles; nest locations depend upon availability.
Abandonment of old colonies and formation of new ones is a typical and
fairly rapid process in wood storks (Frederick and Meyer 2008 p.12).
Most wood stork colonies in the Southeast U.S. have relatively short
survival histories and only a handful of colonies have survived more
than 20 years and the large numbers of short-lived colonies indicate
that wood stork colony abandonment and novel colony initiation seems to
be typical of the species (Tsai et al. 2011, p. 2). The wood storks'
ability to seek out new locations for nesting would seem to indicate
that they will respond in a similar fashion to changes in habitat
availability that result from sea level rise.
Although many species already listed as endangered or threatened
may be particularly vulnerable to negative effects related to changes
in climate, we also recognize that, for some listed species, the likely
effects may be positive or neutral. At this time, we have no evidence
that climate changes observed to date have had any adverse effect on
the wood stork or its habitat; this long-lived species is expected to
adapt to future changes in habitat availability that may result from
climate change.
Contamination Events
Contamination events can be triggered by restoration or natural
events, such as hurricanes or flooding, that can expose concentrations
of contaminants. For example, from November 1998 through early April
1999, a bird mortality event occurred on the north shore of Lake
Apopka, Florida, on former farmlands that had been purchased by the St.
Johns River Water Management District and NRCS. An estimated 676 birds
died on-site, mostly white pelicans (Pelecanus erythrorhynchos) and
various species of wading birds, including the wood stork. Of the
estimated 1,991 wood storks present in the area, 43 died on-site
(Rauschenberger 2007, p. 16). The cause of death was attributed to
organochlorine pesticide (OCP) toxicosis (Rauschenberger 2007, p. 16).
The birds were exposed to OCPs by eating OCP-contaminated fish, which
became easy prey as fish moved from ditches into the flooded fields,
located in the eastern part of the restoration area (Rauschenberger
2007, p. 16).
Mercury, heavy metals, and other contaminants that may impair
reproduction and cause other health issues are being studied in wood
storks and many other wading bird species (Bryan et al. 2012; Gallaher
et al. 2011; Martin 2010; Frederick and Jayasena 2010; Brant et al.
2002; Bryan et al. 2001; Gariboldi et al. 2001). Also, exposure to
contaminants by foraging in manmade wetlands may pose a potential risk
to wood stork health and reproduction. On the other hand, pesticide
contamination has not generally been considered to adversely affect
wood stork reproduction (Ohlendorf et al. 1978, p. 616).
Algal Blooms (Red Tide Events)
Harmful algal blooms, specifically red tide events, have become
more prevalent along Florida's coast. Brevitoxicosis was documented in
2005 as the cause of death of a wood stork (Spalding 2006). Wood storks
can be exposed to harmful microalgae and their toxins through a variety
of mechanisms, including aerosolized transport (i.e., respiratory
irritation in mammals, turtles, birds); bioaccumulation through
consumption of prey containing toxins or toxic cells (crustaceans,
gastropods, fish, birds, turtles, mammals); and mechanical damage by
spines, setae, or other anatomical features of the cells (FWC 2007, p.
1). In addition to dead fish, large numbers of aquatic birds,
particularly double-crested cormorants (Phalacrocorax auritus), red-
breasted mergansers (Mergus merganser), and lesser scaup (Aythya
affinis), were found moribund or dead in red tide areas during the
Florida west coast Karenia brevis red tide of October 1973 to May 1974
(FWC 2007).
Electrocution
Electrocution mortalities of wood storks from power lines have been
documented and reported to us by power companies and by State and
Federal wildlife law enforcement. In most cases, when a problem
location is identified, it is retrofitted using standard avian
protection guidelines to prevent electrocutions. The guidelines
recommend using heavily insulated wire, spreading the wires apart to
prevent grounding as body parts touch the wires, or burying the wires
underground. The Service's Wood Stork Habitat Management Guidelines
(Ogden 1990) include recommendations that new transmission lines be at
least 1 mile away from colony sites and tall transmission towers no
closer than 3 miles from active colonies. The Service also recommends
similar guidance for cell phone towers and wind turbines.
Other Threats
The following is a list of threats that have also been documented
to occur, but we have concluded that due to low incident numbers and
minimal documentation, the impacts at this time are very low and do not
impede recovery.
Human disturbance is known to have a detrimental effect on wood
stork nesting (Service 1997, pp. 10, 12). Wood storks have been
documented to desert nests when disturbed by humans, thus exposing eggs
and young birds to the elements and to predation by gulls and fish
crows (Coulter et al. 1999, p. 19).
Documentation of road kill mortalities of wood storks has increased
(B. Brooks, USFWS, pers. comm., 2010). This may be due to better
reporting or more storks using roadside ponds, ditches, swales, and
flow-ways as foraging habitat.
Stochastic events, such as severe thunderstorms and hurricanes,
pose a potential risk. Loss of nesting trees due to hurricanes can have
a negative impact on nesting habitat. Severe local storm events have
impacted individual colonies, causing chick mortality and even blowing
nests out of trees.
The invasion of exotic plants into natural wetland areas can
prevent wood storks from foraging due to high density and canopy cover
of the plants (USFWS 2010, p. 127). Invasion into natural nesting
habitats by exotic species, including Brazilian pepper (Schinus
terebinthifolius), melaleuca (Melaleuca quinquenervia), and Australian
pine (Casuarina equisetifolia), may present a problem; however, wood
storks are using exotic species for nesting habitat at many manmade
wetland colony sites, such as borrow pits. Even though wetlands
overgrown with exotics may preclude wood storks from foraging within,
they do have a conservation benefit as they flood during the wet season
and provide a prey source to adjacent wetlands. Wood storks are also
documented utilizing Brazilian pepper as nesting substrate (USFWS 1999,
p. 4-396).
A small number of sacred ibis (Threskiornis aethiopicus) escaped
from a south Florida zoo and established a small breeding population in
south Florida. They may compete with wood storks for nesting space
within south Florida colonies.
Summary of Factor E
In summary, other natural or manmade factors affecting the wood
stork's continued existence, such as contaminants, harmful algal
blooms,

[[Page 75961]]

electrocution, road kill, invasion of exotic plants and animals, human
disturbance, and stochastic events, are all documented at minimal
levels to affect wood storks. The wood stork utilizes a wide variety of
habitats throughout its range in the southeastern United States; this
ability to use alternative habitats (as evidenced by the wood storks
expansion from the Everglades of Florida into marshes and tidal areas
throughout the southeastern United States (Brooks and Dean 2008)),
helps to buffer this species from some of the impacts to its habitat
through natural or manmade threats. We conclude that other natural or
manmade factors are not a significant factor affecting the continental
U.S. wood stork DPS, now or in the foreseeable future.

Conclusion

Whether a species is currently on the brink of extinction in the
wild depends on the life history and ecology of the species, the nature
of the threats, and the species' response to those threats. Loss,
fragmentation, and modification of wetland habitats continue as threats
to continental U.S. wood storks. Based on the best available scientific
information, it is our assessment that the species is showing the
ability to respond to these threats through expanding its range,
adjusting its reproductive timing, and utilizing a variety of wetlands,
including manmade wetlands, to forage, roost, and breed. Current data
show that the breeding range has now almost doubled in extent and
shifted northward along the Atlantic coast as far as southeastern North
Carolina. As a result, dependence of wood storks on any specific
wetland complex has been reduced. Even though habitat destruction and
modification are still a threat to recovery, the improved wood stork
population statistics also suggest that wetland habitat is not yet
limiting the population, at least at the landscape level.
A number of regulatory mechanisms are being implemented by Federal
and State agencies to protect wood storks and conserve their habitat.
Take of wood storks is illegal under both the Act and MBTA. Whether
habitat protection and conservation mechanisms are inadequate must be
assessed in terms of the wood stork population. Recent trends indicate
that the range of the continental U.S. wood stork DPS is expanding and
that the breeding population has increased, suggesting that existing
regulatory mechanisms are adequate to allow population growth. However,
we remain concerned that the status of this species would be expected
to deteriorate should the Act's requirements to consult on all federal
actions affecting the species' habitat or the prohibition on take
(including significant habitat modification) be removed.
Other threats such as overutilization of the species for
commercial, recreational, scientific, or educational purposes; disease
and predation; and other natural or manmade factors (e.g.,
contaminants, harmful algal blooms, electrocution, road kill, invasion
of exotic plants and animals, human disturbance, and stochastic events)
are known to occur but are not significant.
While there continue to be ongoing threats, the continental U.S.
wood stork DPS is increasing and expanding its overall range.
Population criteria for reclassification have been exceeded with 3-year
population averages higher than 6,000 nesting pairs since 2003 (range
of 7,086 to 8,996 nesting pairs). Delisting criteria of 10,000 nesting
pairs (5-year average) has not been achieved. The wood stork population
has exceeded 10,000 nesting pairs twice during the past 5 years (2006
and 2009), and the 2009 count of 12,720 nesting pairs represents the
highest count since the early 1960s. Productivity, though variable, is
sufficient to support a growing population. Based on the analysis
presented above and the fact that downlisting criteria have been met,
we believe the continental U.S. wood stork DPS is not presently in
danger of extinction throughout its range. However, because loss,
fragmentation, and modification of wetland habitats continue around
nesting colonies and core foraging areas, and because delisting
criteria have not been met, we conclude that the continental U.S. wood
stork DPS is likely to become endangered within the foreseeable future
and therefore should be reclassified as threatened under the Act.

Significant Portion of the Range Analysis

Having determined that the continental U.S. wood stork DPS meets
the definition of threatened, we must next consider whether there is a
significant portion of the range where the wood stork is in danger of
extinction. The phrase ``significant portion of its range'' (SPR) is
not defined by the statute, and we have never addressed in our
regulations: (1) The consequences of a determination that a species is
either endangered or likely to become so throughout a significant
portion of its range, but not throughout all of its range; or (2) what
qualifies a portion of a range as ``significant.''
Two recent district court decisions have addressed whether the SPR
language allows the Service to list or protect less than all members of
a defined ``species'': Defenders of Wildlife v. Salazar, 729 F. Supp.
2d 1207 (D. Mont. 2010), concerning the Service's delisting of the
Northern Rocky Mountain gray wolf (74 FR 15123, April 2, 2009); and
WildEarth Guardians v. Salazar, 2010 U.S. Dist. LEXIS 105253 (D. Ariz.
Sept. 30, 2010), concerning the Service's 2008 finding on a petition to
list the Gunnison's prairie dog (73 FR 6660, February 5, 2008). The
Service had asserted in both of these determinations that it had
authority, in effect, to protect only some members of a ``species,'' as
defined by the Act (i.e., species, subspecies, or DPS), under the Act.
Both courts ruled that the determinations were arbitrary and capricious
on the grounds that this approach violated the plain and unambiguous
language of the Act. The courts concluded that reading the SPR language
to allow protecting only a portion of a species' range is inconsistent
with the Act's definition of ``species.'' The courts concluded that
once a determination is made that a species (i.e., species, subspecies,
or DPS) meets the definition of ``endangered species'' or ``threatened
species,'' it must be placed on the list in its entirety and the Act's
protections applied consistently to all members of that species
(subject to modification of protections through special rules under
sections 4(d) and 10(j) of the Act).
Consistent with that interpretation, and for the purposes of this
proposed rule and finding, we interpret the phrase ``significant
portion of its range'' in the Act's definitions of ``endangered
species'' and ``threatened species'' to provide an independent basis
for listing a species in its entirety; thus there are two situations
(or factual bases) under which a species would qualify for listing: A
species may be endangered or threatened throughout all of its range; or
a species may be endangered or threatened in only a significant portion
of its range. If a species is in danger of extinction throughout an
SPR, it, the species, is an ``endangered species.'' The same analysis
applies to ``threatened species.'' Therefore, the consequence of
finding that a species is endangered or threatened in only a
significant portion of its range is that the entire species will be
listed as endangered or threatened, respectively, and the Act's
protections will be applied across the species' entire range.
We conclude, for the purposes of this proposed rule and finding,
that interpreting the SPR phrase as providing

[[Page 75962]]

an independent basis for listing is the best interpretation of the Act
because it is consistent with the purposes and the plain meaning of the
key definitions of the Act; it does not conflict with established past
agency practice (i.e., prior to the 2007 Solicitor's Opinion), as no
consistent, long-term agency practice has been established; and it is
consistent with the judicial opinions that have most closely examined
this issue. Having concluded that the phrase ``significant portion of
its range'' provides an independent basis for listing and protecting
the entire species, we next turn to the meaning of ``significant'' to
determine the threshold for when such an independent basis for listing
exists.
Although there are potentially many ways to determine whether a
portion of a species' range is ``significant,'' we conclude, for the
purposes of this proposed rule and finding, that the significance of
the portion of the range should be determined based on its biological
contribution to the conservation of the species. For this reason, we
describe the threshold for ``significant'' in terms of an increase in
the risk of extinction for the species. We conclude that a biologically
based definition of ``significant'' best conforms to the purposes of
the Act, is consistent with judicial interpretations, and best ensures
species' conservation. Thus, for the purposes of this proposed rule and
finding, a portion of the range of a species is ``significant'' if its
contribution to the viability of the species is so important that,
without that portion, the species would be in danger of extinction.
We evaluate biological significance based on the principles of
conservation biology using the concepts of redundancy, resiliency, and
representation. Resiliency describes the characteristics of a species
that allow it to recover from periodic disturbance. Redundancy (having
multiple populations distributed across the landscape) may be needed to
provide a margin of safety for the species to withstand catastrophic
events. Representation (the range of variation found in a species)
ensures that the species' adaptive capabilities are conserved.
Redundancy, resiliency, and representation are not independent of each
other, and some characteristic of a species or area may contribute to
all three. For example, distribution across a wide variety of habitats
is an indicator of representation, but it may also indicate a broad
geographic distribution contributing to redundancy (decreasing the
chance that any one event affects the entire species), and the
likelihood that some habitat types are less susceptible to certain
threats, contributing to resiliency (the ability of the species to
recover from disturbance). None of these concepts is intended to be
mutually exclusive, and a portion of a species' range may be determined
to be ``significant'' due to its contributions under any one of these
concepts.
For the purposes of this proposed rule and finding, we determine if
a portion's biological contribution is so important that the portion
qualifies as ``significant'' by asking whether, without that portion,
the representation, redundancy, or resiliency of the species would be
so impaired that the species would have an increased vulnerability to
threats to the point that the overall species would be in danger of
extinction (i.e., would be ``endangered''). Conversely, we would not
consider the portion of the range at issue to be ``significant'' if
there is sufficient resiliency, redundancy, and representation
elsewhere in the species' range that the species would not be in danger
of extinction throughout its range if the population in that portion of
the range in question became extirpated (extinct locally).
We recognize that this definition of ``significant'' establishes a
threshold that is relatively high. On the one hand, given that the
consequences of finding a species to be endangered or threatened in an
SPR would be listing the species throughout its entire range, it is
important to use a threshold for ``significant'' that is robust. It
would not be meaningful or appropriate to establish a very low
threshold whereby a portion of the range can be considered
``significant'' even if only a negligible increase in extinction risk
would result from its loss. Because nearly any portion of a species'
range can be said to contribute some increment to a species' viability,
use of such a low threshold would require us to impose restrictions and
expend conservation resources disproportionately to conservation
benefit: Listing would be rangewide, even if only a portion of the
range of minor conservation importance to the species is imperiled. On
the other hand, it would be inappropriate to establish a threshold for
``significant'' that is too high. This would be the case if the
standard were, for example, that a portion of the range can be
considered ``significant'' only if threats in that portion result in
the entire species' being currently endangered or threatened. Such a
high bar would not give the SPR phrase independent meaning, as the
Ninth Circuit held in Defenders of Wildlife v. Norton, 258 F.3d 1136
(9th Cir. 2001).
The definition of ``significant'' used in this proposed rule and
finding carefully balances these concerns. By setting a relatively high
threshold, we minimize the degree to which restrictions would be
imposed or resources expended that do not contribute substantially to
species conservation. But we have not set the threshold so high that
the phrase ``in a significant portion of its range'' loses independent
meaning. Specifically, we have not set the threshold as high as it was
under the interpretation presented by the Service in the Defenders
litigation. Under that interpretation, the portion of the range would
have to be so important that current imperilment there would mean that
the species would be currently imperiled everywhere. Under the
definition of ``significant'' used in this proposed rule and finding,
the portion of the range need not rise to such an exceptionally high
level of biological significance. (We recognize that if the species is
imperiled in a portion that rises to that level of biological
significance, then we should conclude that the species is in fact
imperiled throughout all of its range, and that we would not need to
rely on the SPR language for such a listing.) Rather, under this
interpretation we ask whether the species would be endangered
everywhere without that portion, i.e., if that portion were completely
extirpated. In other words, the portion of the range need not be so
important that even being in danger of extinction in that portion would
be sufficient to cause the remainder of the range to be endangered;
rather, the complete extirpation (in a hypothetical future) of the
species in that portion would be required to cause the remainder of the
range to be endangered.
The range of a species can theoretically be divided into portions
in an infinite number of ways. However, there is no purpose to
analyzing portions of the range that have no reasonable potential to be
significant and threatened or endangered. To identify only those
portions that warrant further consideration, we determine whether there
is substantial information indicating that: (1) The portions may be
``significant,'' and (2) the species may be in danger of extinction
there or likely to become so within the foreseeable future. Depending
on the biology of the species, its range, and the threats it faces, it
might be more efficient for us to address the significance question
first or the status question first. Thus, if we determine that a
portion of the range is not ``significant,'' we do not need to

[[Page 75963]]

determine whether the species is endangered or threatened there; if we
determine that the species is not endangered or threatened in a portion
of its range, we do not need to determine if that portion is
``significant.'' In practice, a key part of the portion status analysis
is whether the threats are geographically concentrated in some way. If
the threats to the species are essentially uniform throughout its
range, no portion is likely to warrant further consideration. Moreover,
if any concentration of threats applies only to portions of the
species' range that clearly would not meet the biologically based
definition of ``significant,'' such portions will not warrant further
consideration.
Applying the process described above, we evaluated the continental
U.S. wood stork DPS's range to determine if any areas could be
considered a significant portion of its range, and a key portion of
that determination is whether the threats are geographically
concentrated in some manner. As detailed in the threat analysis in this
proposed rule and finding, the primary threat to the wood stork--
habitat loss, fragmentation, and modification--is a relatively uniform
threat across the species' range.
It could be argued that at the time of listing, the threat of
habitat destruction and fragmentation to the continental U.S. wood
stork DPS at one time was concentrated in south Florida. With the
current habitat regimes, nesting wood storks have persisted in south
Florida with nesting numbers below historic counts but also varying
annually from hundreds to several thousand in many years (Table 2).
Even though we share above that no concentration of threats currently
occurs in the range of this DPS, we provide here more detail on south
Florida to show further why it is not a significant portion of range
because of the emphasis on south Florida in the wood stork recovery
plan.
The wood storks nesting in south Florida (the region south of Lake
Okeechobee from Lee County on the west coast to Palm Beach County on
the east coast, and the Everglades and Big Cypress systems) now
represent approximately 25 percent of the breeding wood storks in the
United States during the past 10 years (Tables 1 and 2). Total nesting
pairs in this region have been quite variable, but showed a general
pattern of decline during the 1970s and remained low through the mid
1980s. However, wood stork nesting increased in south Florida from the
mid 1990s (an average of 400 to 500 pairs) to a high of 5,816 pairs in
2009. A 3-year running average since the time of listing in 1984 ranges
from 457 to 3,449 pairs, with considerable variability. These observed
fluctuations in the nesting between years and nesting sites have been
attributed primarily to variable hydrologic conditions during the
nesting season (Crozier and Gawlik 2003, p. 1; Crozier and Cook 2004,
pp. 1-2). Frequent, heavy rains during nesting can cause water levels
to increase rapidly. The abrupt increases in water levels during
nesting, termed reversals (Crozier and Gawlik 2003, p. 1), may cause
nest abandonment, re-nesting, late nest initiation, and poor fledging
success. For example, optimal foraging conditions in 2006 resulted in
high nesting success, but the 2-year drought that followed in 2007 and
2008 resulted in no nesting success in the Corkscrew Sanctuary rookery
(Lauritsen 2007, p. 11; Lauritsen 2008, p. 12). However, 2009 nesting
data for Corkscrew Sanctuary rookeries noted 1,120 nests producing
2,570 nestlings (Lauritsen 2009, p. 13). Similar rebounds in nesting
activity were recorded for other south Florida rookeries in 2009, with
possibly the largest number of nest starts since 1975, estimated at
about 4,000 nests throughout the Everglades and Big Cypress Systems
(Newman 2009, p. 51) and a total of 5,816 nesting pairs (Table 2) in
south Florida.
The CERP established performance measures and related goals for
wood storks and other wading bird species. Metrics include the number
of pairs of nesting wood storks and the location of the wood stork
colonies. The timing of nesting, which shifted from historical periods
of November through December to January through March, is also a
metric. There have been some recent positive measures in Everglades
restoration regarding these metrics. Restoration predicts that the
return of natural flows and hydrologic patterns will result in large,
sustainable breeding wading bird populations, with large colonies in
the coastal zone of the Everglades and a return to natural timing of
nesting, with wood stork nest initiation in November or December. Cook
and Kobza (2010, p. 2) suggest that Everglades National Park may be
more attractive to nesting birds in recent years and that the 2009
breeding season was the best nesting year in south Florida since the
1940s. The 2009-2010 nesting year did show an improvement in nest
timing with wood stork nesting in January, which is earlier than
previous years, but which is still outside the nesting onset target of
November to December (Newman 2009, p. 52; Gottlieb 2010, p. 42). Also,
Cook and Kobza (2010, p. 2) report a general shift of colony locations
to the coast in recent years.
Although the variability of habitat conditions affects the nesting
efforts in south Florida and at times there is total failure of a
colony or little to no nesting, we do not believe such variability will
cause extirpation of wood storks in south Florida. Wood storks are a
long-lived species that demonstrate considerable variation in
population numbers in response to changing hydrological conditions
(USFWS 1997, p. 10). We are not aware of any other threat within this
portion of the range that would act synergistically and heighten our
level of concern for the wood stork population. Consequently, although
we recognize that it is desirable to improve the nesting success of
wood storks in south Florida, we conclude that the present level of
habitat threat, when combined with the restoration efforts of CERP, is
not of a magnitude that leads us to delineate the wood storks in and
around south Florida as being more in danger of extinction than wood
storks breeding in central/north Florida through North Carolina, nor as
being a significant portion of the range of the continental U.S. wood
stork DPS.
In summary, the primary threat to the continental U.S. wood stork
DPS--habitat loss, fragmentation, and modification--is relatively
uniform throughout the DPS's range. We have determined that none of the
existing or potential threats currently place the continental U.S. wood
stork DPS in danger of extinction throughout all or a significant
portion of its range.

Available Conservation Measures

Conservation measures provided to species listed as endangered or
threatened under the Act include recognition, recovery actions,
requirements for Federal protection, and prohibitions against certain
practices. Recognition through listing increases public awareness of
threats to the continental U.S. breeding population of the wood stork,
and promotes conservation actions by Federal, State, and local
agencies, private organizations, and individuals. The Act provides for
possible land acquisition and cooperation with the State, and for
recovery planning and implementation. The protection required of
Federal agencies and the prohibitions against taking and harm are
discussed, in part below.
A number of the nesting colonies of the continental U.S. wood stork
DPS occur on Federal conservation lands and are consequently afforded
protection

[[Page 75964]]

from development and large-scale habitat disturbance. Wood stork
colonies also occur on a variety of State-owned properties, and
existing State and Federal regulations provide protection on these
sites. There is also a significant number of wood stork colonies that
occur on private lands, and through conservation partnerships, many of
these colonies are protected through the owners' stewardship. In many
cases these partnerships have been developed through conservation
easements, wetland restoration projects, and other conservation means.
The fact that wood stork habitat is primarily wetlands also assures the
opportunity for conference or consultation on most projects that occur
in wood stork habitat under the authorities described below.
Section 7(a) of the Act, as amended, requires Federal agencies to
evaluate their actions with respect to the continental U.S. breeding
population of the wood stork. If a Federal action may affect the wood
stork or its habitat, the responsible Federal agency must consult with
the Service to ensure that any action authorized, funded, or carried
out by such agency is not likely to jeopardize the continued existence
of the wood stork. Federal agency actions that may require consultation
with us include Corps' involvement in projects such as residential
development, mining operations, construction of roads and bridges, or
dredging that requires dredge/fill permits. Protecting and restoring
wetlands that wood storks are dependent upon through the environmental
regulatory review process is the most important action that Federal,
State, and local regulatory agencies can undertake and is key to wood
stork recovery.
The Act and its implementing regulations set forth a series of
general prohibitions and exceptions that apply to all endangered and
threatened wildlife. As such, these prohibitions would be applicable to
the wood stork. These prohibitions, under 50 CFR 17.21 (17.31 for
threatened wildlife species), make it illegal for any person subject to
the jurisdiction of the United States to ``take'' (including to harass,
harm, pursue, hunt, shoot, wound, kill, trap, capture, collect, or to
attempt any of these) within the United States or upon the high seas,
import or export, deliver, receive, carry, transport, or ship in
interstate or foreign commerce in the course of a commercial activity,
or to sell or offer for sale in interstate or foreign commerce, any
endangered wildlife species. It also is illegal to possess, sell,
deliver, carry, transport, or ship any such wildlife that has been
taken in violation of the Act. Certain exceptions apply to agents of
the Service and State conservation agencies.
We may issue permits to carry out otherwise prohibited activities
involving threatened wildlife species under certain circumstances.
Regulations governing permits are codified at Sec. 17.32 for
threatened species. Such permits are available for scientific purposes,
to enhance the propagation or survival of the species, and for
incidental take in the course of otherwise lawful activities. For
threatened species, permits are also available for zoological
exhibition, educational purposes, and special purposes consistent with
the purposes of the Act.
Questions regarding whether specific activities will constitute a
violation of section 9 of the Act should be directed to the U.S. Fish
and Wildlife Service, North Florida Ecological Services Field Office
(see FOR FURTHER INFORMATION CONTACT section). Requests for copies of
the regulations regarding listed species and inquiries about
prohibitions and permits may be addressed to the U.S. Fish and Wildlife
Service, Ecological Services Division, 1875 Century Boulevard, Suite
200, Atlanta, GA 30345 (telephone 404-679-7313, facsimile 404-679-
7081).

Effects of This Rule

This rule, if made final, would revise 50 CFR 17.11(h) to
reclassify the continental U.S. wood stork DPS from endangered to
threatened on the List of Endangered and Threatened Wildlife. This
proposed rule discusses how the continental U.S. wood stork DPS is no
longer in danger of extinction throughout all or a significant portion
of its range. However, this reclassification would not significantly
change the protection afforded this species under the Act. Based on new
information about the range of the continental U.S. wood stork DPS and
where nesting is now occurring, this rule, if made final, would also
revise 50 CFR 17.11(h) to reflect that the range of the continental
U.S. wood stork DPS has expanded from Alabama, Florida, Georgia, and
South Carolina to also include North Carolina and Mississippi (see
Distinct Vertebrate Population Segment Analysis section above).
Anyone taking, attempting to take, or otherwise possessing a wood
stork, or parts thereof, in violation of section 9 of the Act is
subject to a penalty under section 11 of the Act. Pursuant to section 7
of the Act, all Federal agencies must ensure that any actions they
authorize, fund, or carry out are not likely to jeopardize the
continued existence of the continental U.S. wood stork DPS.
If this proposed rule is made final and the continental U.S. wood
stork DPS is reclassified as threatened, recovery actions directed at
the wood stork would continue to be implemented as outlined in the
recovery plan (Service 1997). Highest priority recovery actions
include: (1) Locate nesting habitat; (2) locate roosting and foraging
habitat; (3) inform landowners; (4) protect (nesting) sites from
disturbance; (5) use existing regulatory mechanisms to protect habitat;
and (6) monitor productivity of stork populations. Other recovery
initiatives also include appointing a recovery team to update the
recovery plan to ensure the recovery criteria and actions reflect the
most current information on the demographics, range, and habitat needs
of the species.
Finalization of this proposed rule would not constitute an
irreversible commitment on our part. Reclassification of the
continental U.S. wood stork DPS from threatened status back to
endangered status would be possible if changes occur in management,
population status, or habitat, or if other factors detrimentally affect
the DPS or increase threats to the species' survival.

Peer Review

In accordance with our policy published on July 1, 1994 (59 FR
34270), we will solicit the expert opinions of at least three
appropriate and independent specialists for peer review of this
proposed rule. The purpose of such review is to ensure that decisions
are based on scientifically sound data, assumptions, and analysis. We
will send peer reviewers copies of this proposed rule immediately
following publication in the Federal Register. We will invite peer
reviewers to comment, during the public comment period, on the specific
assumptions and conclusions regarding the proposed reclassification to
threatened. We will summarize the opinions of these reviewers in the
final decision document, and we will consider their input, and any
additional information we receive, as part of our process of making a
final decision on the proposal. Such communication may lead to a final
regulation that differs from this proposal.

Required Determinations

Paperwork Reduction Act of 1995

This rule does not contain any new collections of information that
require approval by the Office of Management and Budget (OMB) under the
Paperwork

[[Page 75965]]

Reduction Act (44 U.S.C. 3501 et seq.). This rule will not impose
recordkeeping or reporting requirements on State or local governments,
individuals, businesses, or organizations. An agency may not conduct or
sponsor, and a person is not required to respond to, a collection of
information unless it displays a currently valid OMB control number.

National Environmental Policy Act

We have determined that we do not need to prepare an environmental
assessment or environmental impact statement, as defined in the
National Environmental Policy Act of 1969 (42 U.S.C 4321 et seq.), in
connection with regulations adopted pursuant to section 4(a) of the
Endangered Species Act. We published a notice outlining our reasons for
this determination in the Federal Register on October 25, 1983 (48 FR
49244).

Government-to-Government Relationship With Tribes

In accordance with the President's memorandum of April 29, 1994,
``Government-to-Government Relations with Native American Tribal
Governments'' (59 FR 22951), Executive Order 13175, and the Department
of the Interior Manual Chapter 512 DM 2, we have considered possible
effects on and have notified the Native American Tribes within the
range of the continental U.S. breeding population of the wood stork
about this proposal. They have been advised through a written
informational mailing from the Service. If future activities resulting
from this proposed rule may affect Tribal resources, a Plan of
Cooperation will be developed with the affected Tribe or Tribes.

Clarity of This Regulation (E.O. 12866)

We are required by Executive Orders 12866 and 12988 and by the
Presidential Memorandum of June 1, 1998, to write all rules in plain
language. This means that each rule we publish must:
(a) Be logically organized;
(b) Use the active voice to address readers directly;
(c) Use clear language rather than jargon;
(d) Be divided into short sections and sentences; and
(e) Use lists and tables wherever possible.
If you feel that we have not met these requirements, send us
comments by one of the methods listed in the ADDRESSES section. To
better help us revise the rule, your comments should be as specific as
possible. For example, you should tell us the numbers of the sections
or paragraphs that are unclearly written, which sections or sentences
are too long, the sections where you feel lists or tables would be
useful, etc.

References Cited

A complete list of references cited is available upon request from
the North Florida Ecological Services Field Office (see FOR FURTHER
INFORMATION CONTACT).

Authors

The primary authors of this document are the staff members of the
North Florida Ecological Services Field Office (see FOR FURTHER
INFORMATION CONTACT).

List of Subjects in 50 CFR Part 17

Endangered and threatened species, Exports, Imports, Reporting and
recordkeeping requirements, Transportation.

Proposed Regulation Promulgation

We propose to amend part 17, subchapter B of chapter I, title 50 of
the Code of Federal Regulations, as set forth below:

PART 17--[AMENDED]

1. The authority citation for part 17 continues to read as follows:

Authority: 16 U.S.C. 1361-1407; 16 U.S.C. 1531-1544; 16 U.S.C.
4201-4245; Pub. L. 99-625, 100 Stat. 3500; unless otherwise noted.

2. Amend Sec. 17.11(h) by revising the entry for ``Stork, wood''
under ``BIRDS'' in the List of Endangered and Threatened Wildlife to
read as follows:

Sec. 17.11 Endangered and threatened wildlife.

* * * * *
(h) * * *

--------------------------------------------------------------------------------------------------------------------------------------------------------
Species Vertebrate population
----------------------------------------------------------- Historic range where endangered or Status When Critical Special
Common name Scientific name threatened listed habitat rules
--------------------------------------------------------------------------------------------------------------------------------------------------------

* * * * * * *
BIRDS

* * * * * * *
Stork, wood........................ Mycteria americana... U.S.A. (CA, AZ, TX, U.S.A. (AL, FL, GA, T 142, NA NA
to Carolinas), MS, NC, SC).
Mexico, C. and S.
America.

* * * * * * *
--------------------------------------------------------------------------------------------------------------------------------------------------------

[[Page 75966]]

* * * * *
Dated: December 14, 2012.
Rowan W. Gould,
Acting Director, Fish and Wildlife Service.
[FR Doc. 2012-30731 Filed 12-21-12; 4:15 pm]
BILLING CODE 4310-55-P