Final
Report of the Bird Inventory:
Fort Donelson
National Battlefield, 20032005
Stephen J. Stedman, Ph. D. 1
Barbara H. Stedman 2
1
Department of English
Tennessee Technological University
Cookeville, TN 38505
sstedman@tntech.edu
2
2675 Lakeland Dr.
Cookeville, TN 38506
Table
of Contents
Lists
of Figures and Tables......................................................................................................
Acknowledgments...........................................................................................
Introduction...........................
.............................................................................................................
Description
of Study Site.......
....................
.............................
...............................................
....
MethodsBird Inventory Techniques............................................................................................... .
Results...............................
................................................................................................................
Expected Species List............. .......... ............................................................................................. ..
Total Species Inventoried ......................................
Breeding Species Inventoried ..................................... .
Species Composition of the Isolated Units..... ............................................ .................................... ...
Discussion............................................................................................ ........ ................................... .
Comparative Effectiveness of Survey Techniques.............. ...... ................................................... ..
Influence of Weather on Results ........................................ .
Description of Bird Diversity in Terms of Observed and Estimated Species Richness ..........................................
Unexpected Results............................................................................................................................................................
Birds Not Found ........................................
Recommendations for Management and Protection of Significant Habitats ...........................................
Suitability of Habitat
for Persistence of Sensitive Species
...........................................
.
Literature Cited..................................................................,............................... ... .........................................
Appendix A: Tables .......................................... ..
ii
List
of Figures
Figure
1. Photograph of the Cumberland River Downstream from the River
Batteries at Fort Donelson National
Battlefield 10 April 2004 (Stephen J. Stedman)
...
.................................................................
......Cover
List of
Tables
Table
1. Expected species at FODO, based on Robinson and Blunk
(1989).
Table
2. Species,
status, seasonal abundance, and breeding category of birds observed at Fort Donelson National
Battlefield 2003-2005...............................................................................................................................................................
Table 3. Species registered during point counts conducted at 15 plots (10 minutes each) at unlimited distance during the breeding seasons of 2004 (SJS) and 2005 (BHS) at Fort Donelson National Battlefield ..........
iii
Acknowledgments
For coordinating
our fieldwork in the park, Robert Wallace, Resource Manager and Ranger,
deserves many thanks. He was very
helpful, providing much information and making access to all sites within the
park possible. Furthermore, he
asked many questions about managing the park for bird species of special
concern and showed keen interest in learning about the species present in the
park.
All
staff members of the Resource Management Office and Visitor Center of the park
were very helpful whenever called upon, and we thank them for this assistance.
Ranger
Jim Jobe was also helpful in providing information about the features of the
park and in making access to non-public area possible for purposes of
inventorying the parks birds.
This
inventory took place during the tenure of two park superintendents, each of
whom we thank for their assistance. First,
Donald Stephenson sat in on our initial meeting at the park and expressed his
interest in the project, offering any assistance needed for it to run
smoothly. After Donald Stephenson
retired, Steve McCoy became park superintendent.
Although we never met him, we especially appreciated his efforts to
ensure that park personnel worked toward successful nesting of a pair of Bald
Eagles in a very public and much used part of the park.
This nest fledged two eagles whose early lives were witnessed by many
visitors to the park.
The
entire Maintenance Department of the park deserve thanks for actively sharing
information about the birdlife of the park; we especially appreciate their
providing us with the record of American White Pelicans.
Jeff
Hancock (Corps of Engineers) also provided much useful information that led to
the success of the bird inventory. We
especially appreciate gaining access to the park maintenance facility on
Hickman Creek, a site owned by the ACE.
Tom
Diggs assisted us greatly by finding and flagging many of the original plots
where point counts were conducted.
We
are greatly indebted to the staff of the Center for the Management,
Utilization, and Protection of Water Resources at Tennessee Technological
University for high quality management of the fiscal paperwork associated with
this bird inventory. Director
Dennis George, Sandra Pigg, Yvette Clark, Amy Knox and especially Glenda
Sharks and Mary Williford, contributed much to our success.
Finally, we are especially
grateful to Teresa Leibfreid, Inventory
and Monitoring Coordinator for the Cumberland Piedmont Network of the NPS, for
her dedication and support throughout the duration of this bird inventory.
iv
Final
Report of Bird Inventory: Fort Donelson National Battlefield, 2003-2005
Introduction
Fort Donelson National Battlefield (FODO ), established in 1928 to
commemorate the site of the first major Union victory of the Civil War, is a
small National Park Service unit that offers the visiting public a moderately
rich bird fauna resulting from the diversity of habitats found within its
boundaries. Within the battlefield boundaries lies Fort Donelson National
Cemetery, created in 1867 as a burial site for the Union dead resulting from
the victory; it contains about 1780 gravesites not only for Union soldiers
killed in 1862 but also for American soldiers killed during all national wars
and conflicts occurring down to the time of the Vietnam Conflict, and it
remains an active national cemetery today. The purpose of this study was 1) to
inventory the bird species occurring at FODO; and 2) to indicate the status
and relative seasonal abundance of documented species.
Containing a total of 223 hectares (551 acres), this National Park
Service unit is located on the Cumberland River (Lake Barkley) about 1.6 km (1
mi) west of Dover and about 5 km (3 mi) east of the southern portions of Land
Between the Lakes in Stewart County, Tennessee.
A slightly disjunct portion of the battlefield lies just south of Rt.
79 and contains about 5 km (3 mi) of rifle pits originally constructed as part
of the perimeter defenses of the fort and now used as a trail system and
greenway. Another small (0.4
hectares [1 acre]) disjunct site that is part of the battlefield is the
Surrender House (Dover Hotel) located on the east side of Dover just upriver
from the Rt. 79 bridge over the Cumberland River.
In
2003 Congress passed a law expanding the area managed by FODO by up to 2000
acres so as to include two historic fort locations on the Tennessee River: Ft.
Henry (about 18 km [11 mi] west of the main battlefield); and Ft. Herman in
Kentucky. Since details about
these additions to the battlefield were not worked out during the period of
the bird inventory, these sites were not inventoried.
Additionally, some parcels of land to the south of the battlefield that
are now owned by the National Historic Trust and that may one day be added to
the battlefield were not inventoried either.
Rt.
79, a major four-lane highway, runs through the southern part the main
battlefield and brings the sound of heavy traffic, including many large
trucks, to most of its parts. The Cumberland River forms the northern boundary of the park
and carries a fairly large volume of boat traffic, both commercial and
recreational. The noise generated
by these transportation corridors sometimes inhibits effective detection of
birdsong.
Besides
its proximity to major transportation arteries, FODO is also surrounded by an
active community of businesses and private homes.
Many local residents use the park trails and roadways of the
battlefield as a recreational site, and especially as a walking site, at all
hours of day and night. Despite
its heavy use, FODO serves as a largely forested island in an urban area as
far as birds are concerned.
Elevation
in the park ranges from 131 m (432 ft) at the Cumberland River (Lake Barkeley)
to about 200 m (660 ft) near the Visitor Center.
The
Surrender House, the greenway, and the Main Battlefield are described in more
detail below.
The
Surrender House property is bordered by the Cumberland River on two sides;
depending on water level, a small beach is sometimes exposed along the edge of
the property. Around the old hotel building itself most of the area is
mowed, but there is a small wooded bluff along the west boundary with a small
ravine and stream at the bottom. Some
of the trees present on the property are medium-sized and a few are large.
There is a small amount of weedy growth along the rivers edge when
the water is too high for this area to be mowed (the waters edge is
actually owned by the ACE). The whole site serves migrant land birds as a resting site
while the open water adjacent to the site attracts water birds (gulls, herons,
and swallows), and Ospreys have nested on a nearby channel marker.
Several species of birds on the inventory list were found only at this
site during the period of the bird inventory.
The
greenway housing the old rifle pits lies south of Rt. 79.
A trail runs about 3 km (1.5 mi) parallel to Rt. 79 among the
earthworks and trenches. The
trail traverses dry hillsides with mature hardwood forest.
Two small creek crossings and several mowed areas are also present
along the trail. Overall this part of FODO was not found to be attractive to
birds except at the sites where small amounts of shrubby growth was present
near the creeks.
The
Main Battlefield is located mainly north of Rt. 79.
The purpose of the fort constructed at this site was to protect the
Cumberland River batteries from land attack and to protect the supply line
that the river provided to Nashville. At
the time of the battle (1862) all trees within 180 m (200 yd) of the fort were
felled to provide a clear line of fire. Confederate soldiers and slaves built
the original 6.7-hectare (15-acre) earthen fort and 5 km (3 mi) of rifle pits
in seven months; much evidence of these fortifications remains today. Some
large portions of the Main Battlefield are now maintained in mowed fields, as
are large areas near the river batteries and along the rivers edge, but a
few wooded areas on high bluffs are excepted.
The
wooded sections of the Main Battlefield between Rt. 79 and the old fort
include areas with steep slopes leading down to streambeds that are dry except
during wet weather. Cedars and pines are present along with oaks and hickories in
most area. Several trails traverse the ridges and hollows of this section of
the park, crossing two small streams at several places.
The
northwest boundary of the Main Battlefield is located at Hickman Creek, which
is extensively flooded much of the year as a result two factors: Barkley Dam
downstream of the park and a coal-fired steam plant upriver which releases
large volumes of water on a regular basis. The northern boundary of the park
is the Cumberland River (Lake Barkley), which serves as a corridor for inland
barge traffic. Between the river batteries, located on the main river, and the
national cemetery another flooded stream, Indian Creek, is, present; like
Hickman Creek this creek is extensively flooded much of the year, and it is
subject to daily fluctuations in water level amounting to 0.3-0.6 m (1-2 ft).
Additionally, during periods of heavy rainfall, water is released at upstream
dams, bringing flood conditions to Hickman and Indian creeks, as well as the
main river. Contrastingly, during drought conditions, water levels in
these creeks goes down, revealing extensive mudflats. Although the ACE owns the shorelines of the river, the NPS
manages and mows them. The main
river is a natural migration corridor for many species of birds, while the two
creeks afford excellent foraging and roosting areas for many species of
waterbirds. During breeding
season, these creeks and the river attract breeding species that require
riparian habitat.
South
of the national cemetery on Indian Creek an area is used infrequently as a boy
scout camp. Part of this area is
mowed field and part is forested, each attracting a fairly large number of
bird species throughout the year. One
of several deep gullies within the park is located on the northern border of
the boy scout camp, separating it from the cemetery.
Shrub-scrub habitat along the slope of this gully is highly productive
of bird species adapted to this habitat in all seasons.
The
national cemetery in the northeast part of the Main Battlefield is a mowed
area with many gravesites and monuments; many large trees have grown up in
this area, creating a city park effect. Some
old-growth forest is located west and north of the cemetery, and there are
some bluffs and steep drop-offs between the cemetery and the main river,
making the area conducive to the presence of raptors and other soaring
species. East of the national
cemetery is a cemetery of the city of Dover and residential areas.
Several
trails in the Main Battlefield pass through forest and waterside habitats.
One of these trails begins at the Visitor Center; this trail is
characterized by considerable elevational change; it was the only area in the
park where several species of warblers were found during the breeding season.
In
2005 an observation platform was added to the river batteries site, making it
possible to scan a large area of river bottomland.
Most
of the deep water areas along the river are heavily used by fishermen in
boats. The area across the river
from the park, and much of the surrounding countryside, is a hunting and
fishing recreation area. During
hunting season, gunfire can often be heard from Hickman Creek, and heavy
gunfire often erupts from the bottomlands across the river where a large
waterfowl management area is located. Sometimes
flights of ducks depart this area when fired upon, often overflying the river
and park; bald eagles patrol this area during hunting seasons and sometimes
snare downed ducks before duck hunters can get to them.
Overall FODO is small by the standards of many parks, and it is
surrounded by urban sprawl. Roads
in the park are mainly limited by topography to the tops of ridges and away
from steep areas and areas where water barriers are present, especially on the
west, north, and east borders of the park. Four narrow, canopy-covered gravel
roads that are gated to the public lie within the park.
Fragmentation in the park forests is a lesser factor than it is in some
larger parks. For a park of its size, FODO has a large amount of riparian
habitat. All of these factors led
to a moderately large species list, especially of breeding birds, for a park
of the size of FODO.
Methods--Bird
Inventory Techniques
Point counts were the most regimented method of collecting bird data at
this NPS unit. Fifteen point
counts were conducted during early to mid-June in each of two years, 2004 and
2005. The protocol for these
counts entailed standing at the center of a 100-meter diameter plot and
counting all birds heard and seen for 10 minutes; birds were recorded as
occurring at one of four distance intervals (< 25 m; 25-50 m; 50-100 m; and
>100 m) or as flyovers; birds were also recorded as occurring within one of
three temporal intervals (0-3 min; 3-5 min; 5-10 min) (Hamel 1992; Hamel et
al. 1996). Any birds flushed
during approach to the plot center were included among the birds recorded at
the point. Birds believed to have
been already counted at a one point were not counted if detected at an
adjacent point. All birds seen or
heard were recorded on a special point count data form.
All point count data are provided in a supplemental Excel file included
with this report.
A second method used to gather data about the birds of this site was
the migration walk. During spring and fall, these walks were conducted 3-4 times
per season. The walks typically
lasted 1-2 hours and covered a distance of about 1.5 km (1 mi) through habitat
considered to have potential for harboring migrant birds.
All species seen or heard were recorded on a standard field card.
A third method used to gather data about the birds of the site was the
raptor survey. These surveys were undertaken during fall and early winter.
Typically, the survey lasted 2-4 hours during late morning.
A route was driven by automobile along all the roads of the unit,
usually totaling about 15 km. All
raptors (and shrikes) detected were included in the resulting data.
All species seen or heard were recorded on a standard field card.
A fourth method of gathering bird data at this site was the night
survey, a somewhat informal method entailing the use of tape-recorded owl
calls to elicit responses from owls at the site.
Besides owls, nightjars were also detected by night surveys during
summer; woodcocks at all seasons; and Grasshopper Sparrows during spring and
summer. All species seen or heard
were recorded on a standard field card, sometimes in conjunction with data
obtained using the following method.
The fifth and last method of obtaining bird data at this site was the
general inventory, involving less regimented efforts to visit many promising
sites within this NPS unit during the course of a day and to keep track of all
species sighted. During the
breeding period for birds, which includes most of the spring and summer, the
general inventory included efforts to detect breeding evidence of for all
species breeding in the unit. All
species seen or heard and all breeding evidence observed were recorded on a
standard field card. At least 1-2
hours per day were spent in all seasons scanning from the river batteries area
for raptors, for birds flying over and moving along the river, and for herons
coming and going to roosts.
Data obtained during migration walks, raptor surveys, night surveys,
and general inventory surveys are provided in a supplemental Excel file
submitted with this report.
Results
Expected Species List
The
Birds of Stewart County, Tennessee (Robinson and Blunk 1989; Appendix A:
Table 1) lists 284 species of birds that have been observed in Stewart County
where FODO is located, causing this list to be the best available compilation
against which to compare results of the bird inventory at FODO. However, some habitats found within Stewart County do not
occur at all within FODO and others are quite limited in extent by the small
area of this park unit, making birds dependent on those habitats less likely
to occur at FODO than elsewhere in the county.
Nonetheless, we use the entire list in Robinson and Blunk (1989) as the
expected species list for FODO.
During the
inventory period, Barbara H. Stedman (most of the time) and Stephen J. Stedman
(a few times) made visits to the unit on a total of 37 days during all seasons
of the year (11 days during spring; 9 days during summer; 9 days during fall;
and 8 days during winter). In the
course of these visits we observed 175 species (Appendix A: Table 2) by one or
more of the methods described above; one additional speciesAmerican White
Pelicanwas observed in the park by maintenance personnel during the
inventory period (and another speciesGolden-winged Warblerwas recorded
historically [Robinson and Blunk 1989]).
The total of 175 species detected during the two-year inventory in FODO
represents approximately 62% of the 284 species known to have occurred in
Stewart County, Tennessee, as of 1989 (Robinson and Blunk 1989).
Some factors that limited the results of the inventory included
·
Traffic noise from Rt. 79, often as loud as interstate traffic noise;
·
Barge traffic noise on the Cumberland River, often very loud and
sometimes constant during all seasons;
·
Recreational boat disturbance on the main river and on Hickman and Indian
creeks;
·
Gunfire during hunting season, especially directly across the river from
the river batteries;
·
Urban development right up to park boundaries on three sides, probably
inhibiting some species from nesting in otherwise suitable habitat;
·
Mowing of grass to river edge, preventing growth of weedy habitat that
would be attractive to many migrant species;
·
High water during most migration seasons (see Influence of Weather
below).
Breeding Species Inventoried
Evidence of breeding by bird species using the unit was divided into
three categories: possible evidence; probable evidence; and confirmed
evidence. In all, 89 species (Appendix A: Table 2) were placed in one of these
categories, including 20 (22%) possible breeders, 17 (19%) probable breeders,
and 52 (59%) confirmed breeders.
Point counts were conducted during the
breeding period of many species. A total of 44 species was registered during
point counts conducted during mid-June 2004, while 62 species were detected
during point counts conducted in early June 2005.
In all, point count effort led to data for 63 species of birds, all of
which use FODO during the breeding season (Appendix A: Table 3). Detailed data
from the point counts are provided in a supplemental Excel file submitted in
conjunction with this report.
Generally
speaking, the larger and more diverse in habitat a site is, the larger the
number of bird species that will be found in it.
This rule of thumb was generally, but not entirely, borne out be the
data obtained during this survey. The
smallest unit of the park, the Surrender House, was a quite productive area to
bird, more so than the greenway, which is a larger unit of the park, but one
where fewer species were found than at the Surrender House.
The Main Battlefield, with its large amount of riparian habitat and its
considerable forested area, as well as its overall larger size than either of
the other units, produced more species than either of two smaller units.
Discussion
Each
of the five survey techniques used for this inventory was effective for its
purpose, but in terms of generating the largest number of species per unit of
time expended, the general inventory was probably the most effective, followed
by the migration walk and the point count (for breeding species only).
Due to their restricted emphasis, night surveys and raptor surveys
generated fewer species per unit of time expended.
The raptor surveys at FODO produced better than expected results,
possibly because of the presence of good roosting areas and because of the
presence of many overlooks from which to observe them.
Influence of
Weather on Results
An
effort was made to visit FODO during periods when the weather was conducive
for registering the maximum number of species during general inventory work,
migration walks, point counts, night surveys, and raptor surveys, so the
influence of weather on the results of the overall inventory was generally
positive.
Very heavy
rainfall during both years of the inventory prevented mudflat habitat for
shorebirds from developing; the only exception was the fall of 2003.
Flooding during late May 2005 was so great that two local Osprey nests
were washed away: one at the Surrender House and one downstream from the Main
Battlefield. Bottomland nesting birds at FODO, such as Canada Goose and
Prothonotary Warbler, would have been negatively affected by these conditions
also.
The fall of
2004 and the winter of 2004-2005 experienced a severe shortage of mast in the
park as well as in the surrounding region, causing some species to move about
seeking food resources. Some
mast-obligate species may not have been recorded in the park during those
seasons as a result of this factor.
The weather
during both winters of the inventory was quite mild, resulting in an absence
of species of boreal irruptives, such as Evening Grosbeak.
Description of Bird Diversity in
Terms of Observed and Estimated Species Richness
Diversity of bird
species in the park was excellent compared to the diversity we expected.
This result took place despite several factors, including
that were all likely negative in their effects on the
diversity of species observed during the inventory.
Although most of these factors could not be changed easily, a change in
the mowing practices in the park would probably benefit many species of birds
and increase bird diversity even more. Species
that require weedy grassland and shrub-scrub habitats were in especially short
supply in the park.
A testament to the suitability of the park to birdlife was provided by
the fact that a pair of Bald Eagles moved its nest site from downriver to a
very public site near the log huts; even near this public site, they
successfully fledged two young during May 2005.
Another testament to the parks
suitability to birdlife was provided by a pair of Ospreys that nested on a
cellular tower near the park in late May 2005, following the destruction of an
earlier nest that was flooded out. These
Ospreys were observed gathering sticks for their new nest near Buckners
Final Defense, well inside the park.
Unexpected Results
The
relatively dense population of Prothonotary Warblers in the parks riparian
habitat was unexpected but welcome. The
parks management practice of leaving dead snags standing is helpful in
maintaining this population of a declining warbler.
Six species of diurnal
raptorsOsprey, Bald Eagle, Coopers Hawk, Red-shouldered Hawk,
Broad-winged Hawk, and Red-tailed Hawk--were noted in the park during nesting
season, certainly a noteworthy and unexpected density of avian predators.
The high number of some interior forest obligates, such as Barred Owl,
several species of woodpeckers, Acadian Flycatcher, and Wood Thrush, was
unexpected in such a relatively small area.
It was unexpected to find singing Cerulean Warblers at two sites during
June 2005; further monitoring for this species is warranted based on this
finding.
Also unexpected was the presence of two scarce nestersWarbling Vireo
and Baltimore Orioleeast of the river batteries.
Birds
Not Found
In general breeding warblers were in short supply or not found at all.
Grassland
breeding obligates such as Northern Bobwhite, Field Sparrow, and Grasshopper
Sparrow were either absent or present in very small numbers.
Wintering species using the same habitat were also scarce or absent.
Few
shorebirds were found because mudflat habitat was often flooded during the
inventory. This would not be the
case in many future years.
Recommendations for Management and Protection of
Significant Habitats
Suitability
of Habitat for Persistence of Sensitive Species
Probably
the only sensitive species among those in the park for prolonged periods of
time (i.e., breeding or wintering) was the Bald Eagle, a pair of which nested
in the park during 2005. Everyone
in Dover knew about these birds, which were able to nest successfully despite
a lot of mostly harmless attention. The
habitat in the park appears suitable to this species, and there is no reason
why it should not remain as a breeder for some time to come.
Literature
Cited
Hamel, P. B. 1992. The Land
Managers Guide to Birds of the South. The Nature Conservancy and U.S.
Forest Service, Atlanta, Georgia.
Hamel, P. B., W. P. Smith, D.
J. Twedt, J. R. Woehr, E. Morris, R. B. Hamilton, and R. J. Cooper. 1996. A
Land Managers Guide to Point Counts of Birds in the Southeast. Gen.
Tech. Rep. SO-120. New Orleans, LA: U.S.D.A. Forest Service, Southern Research
Station. 39 pp.
Robinson, J. C., and D. W.
Blunk. 1989. The Birds of Stewart County, Tennessee. In Proceedings of the
Contributed Papers Session of the Second Annual Symposium on the Natural
History of the Lower Tennessee and Cumberland River Valleys. A. F. Scott, ed. Center for Field Biology of Land Between the
Lakes, Austin Peay State University, Clarksville, Tennessee.
Appendix A: Tables
Table 1. Expected species at FODO, based on Robinson and Blunk (1989):
Fulvous
Whistling-Duck
Greater
White-fronted Goose
Snow
Goose
Ross's
Goose
Brant
Barnacle
Goose
Canada
Goose
Mute
Swan
Tundra
Swan
Wood
Duck
Gadwall
American
Wigeon
Eurasian
Wigeon
American
Black Duck
Mallard
Blue-winged
Teal
Cinnamon
Teal
Northern
Shoveler
Northern
Pintail
Green-winged
Teal
Canvasback
Redhead
Ring-necked
Duck
Greater
Scaup
Lesser
Scaup
Surf
Scoter
White-winged
Scoter
Black
Scoter
Long-tailed
Duck
Bufflehead
Common
Goldeneye
Hooded
Merganser
Common
Merganser
Red-breasted
Merganser
Ruddy
Duck
Ruffed
Grouse
Wild
Turkey
Northern
Bobwhite
Common
Loon
Pied-billed
Grebe
Horned
Grebe
Double-crested
Cormorant
American
Bittern
Least
Bittern
Great
Blue Heron
Great
Egret
Snowy
Egret
Little
Blue Heron
Tricolored
Heron
Cattle
Egret
Green
Heron
Black-crowned
Night-Heron
Yellow-crowned
Night-Heron
White
Ibis
Glossy
Ibis
Wood
Stork
Black
Vulture
Turkey
Vulture
Osprey
Mississippi
Kite
Bald
Eagle
Northern
Harrier
Sharp-shinned
Hawk
Cooper's
Hawk
Northern
Goshawk
Red-shouldered
Hawk
Broad-winged
Hawk
Red-tailed
Hawk
Rough-legged
Hawk
Golden
Eagle
American
Kestrel
Merlin
Peregrine
Falcon
Yellow
Rail
King
Rail
Virginia
Rail
Sora
Purple
Gallinule
Common
Moorhen
American
Coot
Sandhill
Crane
Black-bellied
Plover
American
Golden-Plover
Semipalmated
Plover
Piping
Plover
Killdeer
Black-necked
Stilt
American
Avocet
Spotted
Sandpiper
Solitary
Sandpiper
Greater
Yellowlegs
Willet
Lesser
Yellowlegs
Upland
Sandpiper
Marbled
Godwit
Sanderling
Semipalmated
Sandpiper
Western
Sandpiper
Least
Sandpiper
White-rumped
Sandpiper
Baird's
Sandpiper
Pectoral
Sandpiper
Dunlin
Stilt
Sandpiper
Buff-breasted
Sandpiper
Short-billed
Dowitcher
Long-billed
Dowitcher
Wilson's
Snipe
American
Woodcock
Wilson's
Phalarope
Red-necked
Phalarope
Franklin's
Gull
Bonaparte's
Gull
Ring-billed
Gull
Herring
Gull
Great
Black-backed Gull
Black-legged
Kittiwake
Least
Tern
Caspian
Tern
Black
Tern
Common
Tern
Forster's
Tern
Rock
Pigeon
Mourning
Dove
Common
Ground-Dove
Yellow-billed
Cuckoo
Black-billed
Cuckoo
Barn
Owl
Eastern Screech-Owl
Great Horned Owl
Snowy
Owl
Barred Owl
Short-eared Owl
Common
Nighthawk
Chuck-will's-widow
Whip-poor-will
Chimney Swift
Ruby-throated Hummingbird
Belted Kingfisher
Red-headed Woodpecker
Red-bellied Woodpecker
Yellow-bellied
Sapsucker
Downy Woodpecker
Hairy Woodpecker
Red-cockaded
Woodpecker
Northern
Flicker
Pileated Woodpecker
Olive-sided
Flycatcher
Eastern Wood-Pewee
Yellow-bellied Flycatcher
Acadian Flycatcher
Alder
Flycatcher
Willow
Flycatcher
Least
Flycatcher
Eastern
Phoebe
Great Crested Flycatcher
Eastern Kingbird
Scissor-tailed
Flycatcher
Loggerhead Shrike
White-eyed
Vireo
Yellow-throated Vireo
Blue-headed
Vireo
Warbling
Vireo
Philadelphia Vireo
Red-eyed Vireo
Blue Jay
American Crow
Common
Raven
Horned
Lark
Purple
Martin
Tree
Swallow
Northern Rough-winged Swallow
Bank Swallow
Cliff Swallow
Barn
Swallow
Carolina
Chickadee
Tufted Titmouse
Red-breasted
Nuthatch
White-breasted Nuthatch
Brown
Creeper
Carolina
Wren
Bewick's
Wren
House
Wren
Winter
Wren
Sedge
Wren
Marsh Wren
Golden-crowned Kinglet
Ruby-crowned Kinglet
Blue-gray
Gnatcatcher
Eastern Bluebird
Veery
Gray-cheeked Thrush
Swainson's Thrush
Hermit Thrush
Wood Thrush
American Robin
Gray Catbird
Northern Mockingbird
Brown Thrasher
European Starling
American
Pipit
Cedar
Waxwing
Blue-winged
Warbler
Golden-winged Warbler
Tennessee Warbler
Orange-crowned Warbler
Nashville Warbler
Northern Parula
Yellow Warbler
Chestnut-sided Warbler
Magnolia Warbler
Cape May Warbler
Black-throated Blue Warbler
Yellow-rumped Warbler
Black-throated Green Warbler
Blackburnian Warbler
Yellow-throated Warbler
Pine Warbler
Prairie Warbler
Palm Warbler
Bay-breasted Warbler
Blackpoll Warbler
Cerulean Warbler
Black-and-white Warbler
American
Redstart
Prothonotary Warbler
Worm-eating Warbler
Ovenbird
Northern Waterthrush
Louisiana Waterthrush
Kentucky Warbler
Connecticut Warbler
Mourning Warbler
Common Yellowthroat
Hooded Warbler
Wilson's Warbler
Canada Warbler
Yellow-breasted Chat
Eastern
Towhee
Bachman's
Sparrow
American
Tree Sparrow
Chipping
Sparrow
Clay-colored
Sparrow
Field Sparrow
Vesper Sparrow
Lark
Sparrow
Savannah
Sparrow
Grasshopper Sparrow
Le
Contes Sparrow
Nelsons
Sharp-tailed Sparrow
Fox
Sparrow
Song
Sparrow
Lincoln's Sparrow
Swamp Sparrow
White-throated
Sparrow
White-crowned Sparrow
Harriss
Sparrow
Dark-eyed Junco
Lapland Longspur
Snow
Bunting
Summer
Tanager
Scarlet Tanager
Northern Cardinal
Rose-breasted
Grosbeak
Blue
Grosbeak
Indigo Bunting
Painted
Bunting
Dickcissel
Bobolink
Red-winged
Blackbird
Eastern Meadowlark
Western
Meadowlark
Rusty
Blackbird
Brewer's Blackbird
Common Grackle
Brown-headed Cowbird
Orchard
Oriole
Baltimore
Oriole
Purple
Finch
House Finch
Red Crossbill
Common
Redpoll
Pine
Siskin
American
Goldfinch
Evening
Grosbeak
House
Sparrow
Table 2.
Species, status, seasonal abundance, and breeding category of birds
observed at Fort Donelson National Battlefield 2003-2005.
* = possible breeding evidence noted; ** = probable breeding evidence
noted; *** = confirmed breeding evidence noted.
Key to abbreviations: PR = permanent resident; SR = summer resident; TR =
transient; UN = unknown status (or difficult
to determine because observations are few); VR = visitor; WR = winter
resident. C = common; FC = fairly common; U
= uncommon; VU = very uncommon; R = rare.
|
Common Name |
Scientific Name |
Status |
Sp |
Su |
Fa |
Wi |
|
|
|
|
|
|
|
|
____ |
Snow
Goose |
Chen
caerulescens |
WR |
|
|
R |
R |
____ |
Canada
Goose ** |
Branta
canadensis |
PR |
FC |
VU |
U |
FC |
____ |
Wood
Duck ** |
Aix
sponsa |
PR |
U |
|
VU |
U |
____ |
Gadwall |
Anas
strepera |
WR |
|
|
R |
|
____ |
American
Wigeon |
Anas
americana |
WR |
|
|
|
VU |
____ |
American
Black Duck |
Anas
rubripes |
WR |
|
|
VU |
VU |
____ |
Mallard |
Anas
platyrhynchos |
PR |
|
|
VU |
U |
____ |
Northern
Shoveler |
Anas
clypeata |
WR |
|
|
|
VU |
____ |
Northern
Pintail |
Anas
acuta |
WR |
|
|
|
R |
____ |
Green-winged
Teal |
Anas
crecca |
WR |
|
|
VU |
|
____ |
Ring-necked
Duck |
Aythya
collaris |
WR |
VU |
|
VU |
VU |
____ |
Bufflehead |
Bucephala
albeola |
WR |
|
|
|
VU |
____ |
Hooded
Merganser |
Dophodytes
cucullatus |
WR |
|
|
|
VU |
____ |
Ruddy
Duck |
Oxyurus
jamaicensis |
WR |
|
|
VU |
|
____ |
Wild
Turkey *** |
Meleagris
gallopavo |
PR |
U |
VU |
VU |
|
____ |
Northern
Bobwhite ** |
Colinus
virginianus |
PR |
U |
VU |
VU |
VU |
____ |
Common
Loon |
Gavia
immer |
VR |
|
|
R |
R |
____ |
Pied-billed
Grebe |
Podilymbus
podiceps |
WR |
VU |
|
|
|
____ |
American
White Pelican # |
Pelecanus
erythrorhynchos |
VR |
R |
|
|
|
____ |
Double-crested
Cormorant |
Phalacrocorax
auritus |
WR |
FC |
|
VU |
|
____ |
Great
Blue Heron * |
Ardea
herodias |
PR |
U |
U |
FC |
FC |
____ |
Great
Egret |
Ardea
alba |
VR |
U |
|
U |
|
____ |
Little
Blue Heron |
Egretta
caerulea |
VR |
U |
VU |
U |
|
____ |
Green
Heron ** |
Butorides
virescens |
SR |
U |
U |
U |
|
____ |
Black-crowned
Night-Heron * |
Nycticorax
nycticorax |
PR |
U |
U |
U |
U |
____ |
Yellow-cr.
Night-Heron *** |
Nyctanassa
violacea |
UN |
|
R |
R |
|
____ |
Black
Vulture |
Coragyps
atratus |
PR |
U |
U |
U |
U |
____ |
Turkey
Vulture |
Cathartes
aura |
PR |
U |
U |
U |
U |
____ |
Osprey
*** |
Pandion
haliaetus |
SR |
U |
U |
U |
R |
____ |
Mississippi
Kite |
Ictinia
mississippiensis |
TR |
|
R |
R |
|
____ |
Bald
Eagle *** |
Haliaeetus
leucocephalus |
WR |
U |
U |
U |
U |
____ |
Northern
Harrier |
Circus
cyaneus |
WR |
|
|
|
R |
____ |
Sharp-shinned
Hawk |
Accipiter
striatus |
WR |
|
|
VU |
U |
____ |
Cooper's
Hawk * |
Accipiter
cooperi |
PR |
VU |
VU |
VU |
U |
____ |
Red-shouldered
Hawk *** |
Buteo
lineatus |
PR |
U |
U |
U |
U |
____ |
Broad-winged
Hawk * |
Buteo
platypterus |
SR |
U |
VU |
U |
|
____ |
Red-tailed
Hawk *** |
Buteo
jamaicensis |
PR |
U |
U |
VU |
U |
____ |
American
Kestrel |
Falco
sparverius |
VR |
|
|
|
R |
____ |
Peregrine
Falcon |
Falco
peregrinus |
TR |
|
|
R |
|
____ |
Semipalmated
Plover |
Charadrius
semipalmatus |
TR |
|
|
VU |
|
____ |
Killdeer
*** |
Charadrius
vociferus |
PR |
U |
U |
U |
U |
____ |
Spotted
Sandpiper |
Actitis
macularius |
TR |
VU |
VU |
U |
|
____ |
Greater
Yellowlegs |
Tringa
melanoleuca |
TR |
|
|
R |
|
____ |
American
Woodcock * |
Scolopax
minor |
PR |
VU |
VU |
VU |
R |
____ |
Bonaparte's
Gull |
Larus
philadelphia |
WR |
|
|
|
VU |
____ |
Ring-billed
Gull |
Larus
delawarensis |
WR |
FC |
|
U |
A |
____ |
Herring
Gull |
Larus
argentatus |
WR |
|
|
|
U |
____ |
Caspian
Tern |
Hydroprogne
caspia |
TR |
|
|
U |
|
____ |
Black
Tern |
Chlidonias
niger |
TR |
|
|
VU |
|
____ |
Forster's
Tern |
Sterna
forsteri |
TR |
VU |
|
|
|
____ |
Rock
Pigeon |
Columba
livia |
PR |
VU |
|
VU |
|
____ |
Mourning
Dove *** |
Zenaida
macroura |
PR |
FC |
C |
C |
U |
____ |
Yellow-billed
Cuckoo ** |
Coccyzus
americanus |
SR |
U |
U |
U |
|
____ |
Black-billed
Cuckoo |
Coccyzus
erythropthalmus |
TR |
VU |
|
|
|
____ |
Eastern
Screech-Owl ** |
Megascops
asio |
PR |
U |
U |
U |
U |
____ |
Great
Horned Owl *** |
Bubo
virginianus |
PR |
U |
U |
U |
U |
____ |
Barred
Owl ** |
Strix
varia |
PR |
U |
U |
U |
U |
____ |
Common
Nighthawk |
Chordeiles
minor |
TR |
R |
|
VU |
|
____ |
Eastern
Whip-poor-will |
Caprimulgus
vociferus |
TR |
R |
|
|
|
____ |
Chimney
Swift * |
Chaetura
pelagica |
SR |
U |
U |
U |
|
____ |
Ruby-throat.
Hummingbird * |
Archilochus
colubris |
SR |
U |
U |
U |
|
____ |
Belted
Kingfisher * |
Ceryle
alcyon |
PR |
U |
U |
U |
U |
____ |
Red-headed
Woodpecker *** |
Melanerpes
erythrocephalus |
PR |
U |
U |
U |
U |
____ |
Red-bellied
Woodpecker *** |
Melanerpes
carolinus |
PR |
FC |
FC |
FC |
FC |
____ |
Yellow-bellied
Sapsucker |
Sphyrapicus
varius |
WR |
U |
|
U |
U |
____ |
Downy
Woodpecker *** |
Picoides
pubescens |
PR |
FC |
U |
FC |
FC |
____ |
Hairy
Woodpecker *** |
Picoides
villosus |
PR |
U |
U |
U |
U |
____ |
Northern
Flicker ** |
Colaptes
auratus |
PR |
U |
U |
U |
U |
____ |
Pileated
Woodpecker *** |
Dryocopus
pileatus |
PR |
U |
U |
FC |
U |
____ |
Eastern
Wood-Pewee *** |
Contopus
virens |
SR |
U |
FC |
U |
|
____ |
Acadian
Flycatcher *** |
Empidonax
virescens |
SR |
U |
FC |
VU |
|
____ |
Eastern
Phoebe *** |
Sayornis
phoebe |
PR |
U |
U |
U |
U |
____ |
Great
Crested Flycatcher *** |
Myiarchus
crinitus |
SR |
U |
U |
VU |
|
____ |
Eastern
Kingbird *** |
Tyrannus
tyrannus |
SR |
U |
U |
VU |
|
____ |
White-eyed
Vireo *** |
Vireo
griseus |
SR |
FC |
FC |
FC |
|
____ |
Yellow-throated
Vireo ** |
Vireo
flavifrons |
SR |
U |
U |
U |
|
____ |
Blue-headed
Vireo |
Vireo
solitarius |
TR |
VU |
|
VU |
|
____ |
Warbling
Vireo * |
Vireo
gilvus |
SR |
VU |
R |
VU |
|
____ |
Philadelphia
Vireo |
Vireo
philadelphicus |
TR |
|
|
R |
|
____ |
Red-eyed
Vireo *** |
Vireo
olivaceous |
SR |
FC |
C |
U |
|
____ |
Blue
Jay *** |
Cyanocitta
cristata |
PR |
FC |
C |
FC |
FC |
____ |
American
Crow ** |
Corvus
brachyrhynchos |
PR |
FC |
C |
C |
FC |
____ |
Purple
Martin |
Progne
subis |
SR |
U |
U |
|
|
____ |
Tree
Swallow ** |
Tachycineta
bicolor |
SR |
U |
VU |
U |
|
____ |
N.
Rough-winged Swallow *** |
Stelgidopteryx
serripennis |
SR |
U |
U |
U |
|
____ |
Bank
Swallow |
Riparia
riparia |
TR |
VU |
|
|
|
____ |
Cliff
Swallow *** |
Petrochelidon
pyrrhonota |
SR |
U |
FC |
U |
|
____ |
Barn
Swallow *** |
Hirundo
rustica |
SR |
U |
FC |
U |
|
____ |
Carolina
Chickadee *** |
Poecile
carolinensis |
PR |
C |
FC |
FC |
A |
____ |
Tufted
Titmouse *** |
Baeolophus
bicolor |
PR |
C |
FC |
FC |
A |
____ |
Red-breasted
Nuthatch |
Sitta
canadensis |
WR |
|
|
|
R |
____ |
White-breasted
Nuthatch *** |
Sitta
carolinensis |
PR |
U |
FC |
FC |
FC |
____ |
Brown
Creeper |
Certhia
americana |
WR |
VU |
|
R |
VU |
____ |
Carolina
Wren *** |
Thryothorus
ludovicianus |
PR |
C |
C |
C |
A |
____ |
House
Wren * |
Troglodytes
aedon |
SR |
VU |
VU |
VU |
|
____ |
Winter
Wren |
Troglodytes hiemalis |
WR |
VU |
|
VU |
U |
____ |
Sedge
Wren |
Cistothorus
platensis |
VR |
|
|
|
R |
____ |
Marsh
Wren |
Cistothorus
palustris |
TR |
|
|
R |
|
____ |
Golden-crowned
Kinglet |
Regulus
satrapa |
WR |
|
|
VU |
U |
____ |
Ruby-crowned
Kinglet |
Regulus
calendula |
WR |
U |
|
VU |
U |
____ |
Blue-gray
Gnatcatcher *** |
Polioptila
caerulea |
SR |
C |
FC |
FC |
|
____ |
Eastern
Bluebird *** |
Sialia
sialis |
PR |
C |
A |
C |
A |
____ |
Veery |
Catharus
fuscescens |
TR |
VU |
|
|
|
____ |
Gray-cheeked
Thrush |
Catharus
minimus |
TR |
R |
|
|
|
____ |
Swainson's
Thrush |
Catharus
ustulatus |
TR |
U |
|
VU |
|
____ |
Hermit
Thrush |
Catharus
guttatus |
WR |
U |
|
VU |
U |
____ |
Wood
Thrush *** |
Hylocichla
mustelina |
SR |
FC |
FC |
VU |
|
____ |
American
Robin *** |
Turdus
migratorius |
PR |
FC |
C |
C |
A |
____ |
Gray
Catbird * |
Dumetella
carolinensis |
SR |
U |
VU |
VU |
|
____ |
Northern
Mockingbird *** |
Mimus
polyglottus |
PR |
U |
FC |
U |
U |
____ |
Brown
Thrasher *** |
Toxostoma
rufum |
PR |
U |
U |
U |
U |
____ |
European
Starling *** |
Sturnus
vulgaris |
PR |
FC |
A |
A |
FC |
____ |
American
Pipit |
Anthus
rubescens |
VR |
|
|
|
R |
____ |
Cedar
Waxwing * |
Bombycilla
cedrorum |
PR |
VU |
U |
U |
U |
____ |
Blue-winged
Warbler |
Vermivora
cyanoptera |
TR |
VU |
|
VU |
|
____ |
Golden-winged
Warbler ## |
Vermivora
chrysoptera |
TR |
|
|
R |
|
____ |
Tennessee
Warbler |
Oreothlypis
peregrina |
TR |
U |
|
VU |
|
____ |
Orange-crowned
Warbler |
Oreothlypis
celata |
TR |
VU |
|
R |
|
____ |
Nashville
Warbler |
Oreothlypis
ruficapilla |
TR |
VU |
|
R |
|
____ |
Northern
Parula *** |
Parula
americana |
SR |
FC |
FC |
VU |
|
____ |
Yellow
Warbler * |
Dendroica
petechia |
SR |
U |
R |
|
|
____ |
Chestnut-sided
Warbler |
Dendroica
pensylvanica |
TR |
U |
|
VU |
|
____ |
Magnolia
Warbler |
Dendroica
magnolia |
TR |
U |
|
VU |
|
____ |
Cape
May Warbler |
Dendroica
tigrina |
TR |
VU |
|
|
|
____ |
Yellow-rumped
Warbler |
Dendroica
coronata |
WR |
FC |
|
FC |
A |
____ |
Black-thr.
Green Warbler |
Dendroica
virens |
TR |
U |
|
VU |
|
____ |
Blackburnian
Warbler |
Dendroica
fusca |
TR |
U |
|
VU |
|
____ |
Yellow-throated
Warbler ** |
Dendroica
dominica |
SR |
U |
U |
U |
|
____ |
Pine
Warbler *** |
Dendroica
pinus |
SR |
U |
U |
U |
|
____ |
Prairie
Warbler ** |
Dendroica
discolor |
SR |
U |
U |
VU |
|
____ |
Palm
Warbler |
Dendroica
palmarum |
TR |
U |
|
VU |
|
____ |
Bay-breasted
Warbler |
Dendroica
castanea |
TR |
VU |
|
VU |
|
____ |
Blackpoll
Warbler |
Dendroica
striata |
TR |
U |
|
|
|
____ |
Cerulean
Warbler * |
Dendroica
cerulea |
SR |
U |
R |
|
|
____ |
Black-and-white
Warbler |
Mniotilta
varia |
TR |
U |
|
VU |
|
____ |
American
Redstart |
Setophaga
ruticilla |
TR |
U |
|
VU |
|
____ |
Prothonotary
Warbler *** |
Protonotaria
citrea |
SR |
U |
U |
VU |
|
____ |
Worm-eating
Warbler * |
Helmitheros
vermivorum |
SR |
U |
VU |
VU |
|
____ |
Ovenbird
* |
Seiurus
aurocapillus |
SR |
U |
VU |
VU |
|
____ |
Northern
Waterthrush |
Parkesia
novaboracensis |
TR |
VU |
|
|
|
____ |
Louisiana
Waterthrush *** |
Parkesia
motacilla |
SR |
U |
VU |
|
|
____ |
Kentucky
Warbler *** |
Oporornis
formosus |
SR |
U |
VU |
R |
|
____ |
Common
Yellowthroat ** |
Geothlypis
trichas |
SR |
U |
U |
U |
|
____ |
Hooded
Warbler * |
Wilsonia
citrina |
SR |
U |
VU |
VU |
|
____ |
Canada
Warbler |
Wilsonia
canadensis |
TR |
VU |
|
|
|
____ |
Yellow-breasted
Chat |
Icteria
virens |
TR |
U |
|
VU |
|
____ |
Eastern
Towhee *** |
Pipilo
erythrophthalmus |
PR |
FC |
C |
FC |
U |
____ |
Chipping
Sparrow *** |
Spizella
passerina |
PR |
C |
A |
C |
U |
____ |
Field
Sparrow * |
Spizella
pusilla |
PR |
U |
VU |
VU |
VU |
____ |
Savannah
Sparrow |
Passerculus
sandwichensis |
WR |
VU |
|
|
VU |
____ |
Grasshopper
Sparrow |
Ammodramus
savannarum |
TR |
R |
|
|
|
____ |
Fox
Sparrow |
Passerella
iliaca |
WR |
VU |
|
|
VU |
____ |
Song
Sparrow |
Melospiza
melodia |
WR |
VU |
|
U |
U |
____ |
Lincoln's
Sparrow |
Melospiza
lincolnii |
TR |
VU |
|
R |
|
____ |
Swamp
Sparrow |
Melospiza
georgiana |
WR |
U |
|
VU |
|
____ |
White-throated
Sparrow |
Zonotrichia
albicollis |
WR |
FC |
|
VU |
A |
____ |
White-crowned
Sparrow |
Zonotrichia
leucophrys |
WR |
R |
|
|
|
____ |
Dark-eyed
Junco |
Junco
hyemalis |
WR |
U |
|
VU |
A |
____ |
Summer
Tanager *** |
Piranga
rubra |
SR |
FC |
FC |
U |
|
____ |
Scarlet
Tanager ** |
Piranga
olivacea |
SR |
U |
U |
U |
|
____ |
Northern
Cardinal *** |
Cardinalis
cardinalis |
PR |
FC |
C |
A |
FC |
____ |
Rose-breasted
Grosbeak |
Pheucticus
ludovicianus |
TR |
U |
|
U |
|
____ |
Blue
Grosbeak * |
Passerina
caerulea |
SR |
U |
VU |
VU |
|
____ |
Indigo
Bunting *** |
Passerina
cyanea |
SR |
FC |
C |
FC |
|
____ |
Bobolink |
Dolichonyx
orizyvorus |
TR |
R |
|
|
|
____ |
Red-winged
Blackbird *** |
Agelaius
phoeniceus |
PR |
U |
U |
VU |
VU |
____ |
Eastern
Meadowlark ** |
Sturnella
magna |
PR |
U |
U |
VU |
VU |
____ |
Rusty
Blackbird |
Euphagus
carolinus |
WR |
|
|
R |
|
____ |
Common
Grackle *** |
Quiscalus
quiscula |
PR |
FC |
C |
U |
U |
____ |
Brown-headed
Cowbird ** |
Molothrus
ater |
PR |
FC |
FC |
VU |
|
____ |
Orchard
Oriole *** |
Icterus
spurius |
SR |
U |
U |
VU |
|
____ |
Baltimore
Oriole * |
Icterus
galbula |
SR |
U |
VU |
|
|
____ |
Purple
Finch |
Carpodacus
purpureus |
WR |
VU |
|
|
U |
____ |
House
Finch *** |
Carpodacus
mexicanus |
PR |
U |
U |
U |
U |
____ |
Pine
Siskin |
Spinus
pinus |
VR |
|
|
|
R |
____ |
American
Goldfinch *** |
Spinus
tristis |
PR |
U |
U |
FC |
U |
____ |
House
Sparrow *** |
Passer
domesticus |
PR |
VU |
VU |
U |
VU |
Table 3.
Species registered during point counts conducted at 15 plots (10 minutes
each) at unlimited distance during the breeding seasons of 2004 (SJS) and 2005 (BHS)
at Fort Donelson National Battlefield. Greater detail about the results of these
point counts is provided in an Excel file that supplements this report.
Inds = total individuals counted.
Species |
|
2004 |
|
2005 |
|
Stops |
Inds |
Stops |
Inds |
|
|
|
|
|
Observer |
|
SJS |
|
BHS |
|
|
|
|
|
Wild Turkey |
-- |
-- |
1 |
1 |
Great Blue Heron |
-- |
-- |
2 |
3 |
Green Heron |
-- |
-- |
1 |
1 |
Osprey |
-- |
-- |
1 |
1 |
Bald Eagle |
-- |
-- |
1 |
1 |
Broad-winged Hawk |
-- |
-- |
1 |
1 |
Mourning Dove |
2 |
2 |
7 |
10 |
Yellow-billed
Cuckoo |
3 |
4 |
4 |
4 |
Great Horned Owl |
-- |
-- |
1 |
1 |
Barred Owl |
-- |
-- |
1 |
1 |
Ruby-throated
Hummingbird |
2 |
2 |
1 |
1 |
Belted Kingfisher |
-- |
-- |
2 |
2 |
Red-headed
Woodpecker |
-- |
-- |
1 |
1 |
Red-bellied
Woodpecker |
10 |
12 |
6 |
10 |
Downy Woodpecker |
5 |
5 |
3 |
3 |
Hairy Woodpecker |
1 |
1 |
2 |
2 |
Northern Flicker |
1 |
1 |
3 |
3 |
Pileated
Woodpecker |
1 |
1 |
2 |
2 |
Eastern Wood-Pewee |
7 |
7 |
5 |
6 |
Acadian Flycatcher |
9 |
17 |
7 |
12 |
Eastern Phoebe |
1 |
1 |
2 |
2 |
Great Crested
Flycatcher |
4 |
5 |
6 |
6 |
Eastern Kingbird |
-- |
-- |
1 |
1 |
White-eyed Vireo |
4 |
6 |
8 |
9 |
Yellow-throated
Vireo |
7 |
9 |
5 |
5 |
Red-eyed Vireo |
15 |
19 |
13 |
25 |
Blue Jay |
4 |
4 |
7 |
14 |
American Crow |
8 |
10 |
3 |
11 |
Purple Martin |
-- |
-- |
2 |
4 |
Barn Swallow |
1 |
1 |
1 |
4 |
Carolina Chickadee |
11 |
14 |
10 |
16 |
Tufted Titmouse |
12 |
15 |
12 |
23 |
White-breasted
Nuthatch |
2 |
2 |
6 |
9 |
Carolina Wren |
12 |
19 |
13 |
30 |
Blue-Gray
Gnatcatcher |
12 |
16 |
7 |
11 |
Eastern Bluebird |
2 |
3 |
7 |
10 |
Wood Thrush |
7 |
11 |
11 |
16 |
American Robin |
1 |
1 |
4 |
7 |
Northern
Mockingbird |
-- |
-- |
2 |
2 |
Brown Thrasher |
1 |
1 |
3 |
5 |
European Starling |
-- |
-- |
1 |
7 |
Cedar Waxwing |
1 |
1 |
1 |
2 |
Northern Parula |
9 |
11 |
4 |
4 |
Yellow-throated
Warbler |
3 |
3 |
3 |
3 |
Pine Warbler |
2 |
2 |
2 |
2 |
Prairie Warbler |
1 |
1 |
-- |
-- |
Prothonotary
Warbler |
3 |
4 |
3 |
6 |
Louisiana
Waterthrush |
-- |
-- |
1 |
1 |
Kentucky Warbler |
6 |
8 |
6 |
7 |
Common
Yellowthroat |
-- |
-- |
2 |
2 |
Eastern Towhee |
3 |
3 |
4 |
6 |
Chipping Sparrow |
1 |
1 |
6 |
15 |
Summer Tanager |
8 |
9 |
12 |
21 |
Scarlet Tanager |
6 |
7 |
5 |
5 |
Northern Cardinal |
10 |
12 |
12 |
38 |
Blue Grosbeak |
-- |
-- |
2 |
2 |
Indigo Bunting |
3 |
6 |
6 |
11 |
Common Grackle |
3 |
3 |
1 |
2 |
Brown-headed
Cowbird |
1 |
1 |
7 |
18 |
Orchard Oriole |
2 |
3 |
4 |
6 |
Baltimore Oriole |
-- |
-- |
1 |
1 |
House Finch |
-- |
-- |
1 |
2 |
American Goldfinch |
5 |
5 |
4 |
8 |
|
|
|
|
|
Total Species |
|
44 |
|
62 |