2.1.1. Species Selection Process
2.1.3. How to Use the Species Accounts
2.2.1. Fishes and Lampreys (Class Actinopterygii and
Cephalaspidomorphi) Overview
2.2.2. Fishes and Lampreys (Class Actinopterygii and
Cephalaspidomorphi) Species Accounts
2.2.3. Mussels (Class Bivalvia) Overview
2.2.4. Mussels (Class Bivalvia) Species Accounts
2.3. TERRESTRIAL SPECIES ACCOUNTS
2.3.1. Amphibians (Class Amphibia) Overview
2.3.2. Amphibians (Class Amphibia) Species Accounts
2.3.3. Birds (Class Aves) Overview
2.3.4. Birds (Class Aves) Species Accounts
2.3.5. Mammals (Class Mammalia) Overview
2.3.6.
Mammals (Class Mammalia) Species Accounts
2.3.7. Reptiles (Class Reptilia) Overview
2.3.8.
Reptiles (Class Reptilia) Species Accounts
Volume II is designed to allow users easy access to information about each of the 251 Species of Greatest Conservation Need (SGCN) addressed in this Plan (Appendix 1.1). All of Elements 1 and 2, along with portions of Element 3 are addressed here. The species selection process is described along with data sources and the species accounts. The KY-CWCS team elected to provide detailed information about each species in the format of species accounts. The following sections explain the organization of the accounts, specific fields in the accounts, legends for the species occurrence maps, and other details to facilitate using this information.
2.1.1. Species Selection Process
Kentucky has a large variety of fish and wildlife species that are supported by equally diverse waterways and ecoregions. This diversity presented a challenge in deciding the appropriate groups and species to include in our Strategy. The CWCS team members considered all groups of vertebrates and invertebrates found in Kentucky with the guiding principles of identifying species and habitats in greatest need of conservation and adequately representing the diversity of habitats and species. The team quickly realized that digital data for invertebrate groups other than bivalves was very sparse. The Kentucky State Nature Preserves Commission (KSNPC) Natural Heritage Database had approximately 900 records for 134 invertebrate taxa (average of 6.7 records per taxa) in the following groups: gastropods, arachnids, crustaceans, diplopods, and insects (Don Dott, pers. comm.). The team also realized that many invertebrate groups could be protected indirectly within the context of our strategy through protection of vertebrate groups and bivalves. An example of this principle is illustrated by Kentucky’s karst region. This area contains several known species of crayfishes, cave beetles, and isopods not included in our CWCS. There are likely several species not yet described by scientists. Many species will profit from conservation actions implemented for the many SGCN found within Priority Conservation Areas (PCAs) identified in Volume IV (e.g., Interior Low Plateau Karst Region, Appendix 4.32). Addressing the caves, streams, and many terrestrial habitats here provides wide ranging benefit to those invertebrates not included in this draft. We recognize that future revisions of this strategy will need to include groups of invertebrates not covered in this draft, especially crayfish, land snails, and lepidopterons. We will work with partners to identify the appropriate groups. Given the scarcity of digital data for most invertebrates and the ability to provide indirect benefits, the CWCS team decided to restrict Kentucky’s species list to terrestrial vertebrates, fishes, lampreys, and bivalves.
Even after narrowing the field as just described nearly 900 species were left to consider (Appendix 2.1). The taxonomic overviews that follow give a more complete discussion of species diversity for each group. The CWCS planning team examined the list of species monitored by the KSNPC (Appendix 2.2). While the list of KSNPC monitored species provided a valuable starting point for species in need of conservation, it did not necessarily cover the diversity of habitats or include many species monitored by other groups. For example, several bird species were added based on information from the Partner’s in Flight Program. Team members ensured that all vertebrate and mussel species with NatureServe Global Ranks (GRank) of G1, G2, and G3 were included. However, great care was taken to ensure the list was not simply a ‘threatened and endangered list’ of species. Over half the species are G4 (apparently secure) or G5 (secure) (Appendix 2.3) and 203 of the 251 species have no status under the Endangered Species Act (Appendix 2.4). Conversely, over half of the species are S1 (critically imperiled) or S2 (imperiled) within Kentucky (Appendix 2.5). Most of these S1 and S2 species also have G4 or G5 rankings. Other criteria for inclusion of vertebrate and mussel species were state endemics, reptile and amphibian species whose status were uncertain, and extirpated species that may be re-introduced. The first draft of this species list was sent to other taxonomic experts for review and modifications were made based on these comments.
A wide variety of data were used to compile the species accounts that fall into two general categories: 1) information for the text portion and, 2) data for species occurrence maps. Each taxonomic group includes a literature section covering references used. In general, NatureServe and The Kentucky State Nature Preserves Commission were widely cited across groups. Also, personal communication with a variety of taxonomic experts was often cited where data or publications were lacking.
Data for mapping were gleaned from 35 sources housed at the Kentucky Department of Fish and Wildlife Resources Fish and Wildlife Information System (KFWIS) that included 22,970 individual observations (Appendix 2.6 and 2.7). The precision of observation data range from points with latitude and longitude coordinates, USGS quadrangle observations, and county level only observations. First draft maps were sent to taxonomic experts for review and questionable occurrence records were flagged for further investigation.
Critical to the effective management of these data were the use of a relational database management system (RDBMS) in conjunction with a geographic information system (GIS). Use of RDBMS allowed species level information (e.g., taxonomy, status, trend, etc.) to be connected with spatial information (e.g., occurrences, habitat, range) using GIS. This allowed CWCS team members to more fully investigate the distribution of single species or groups of species based on criteria such as abundance (GRank or SRank) and habitat guild(s). Use of RDBMS and GIS will be essential to future revisions of the CWCS. This technology will allow for updating of status and distribution information as it becomes available and facilitate the sharing of information with conservation partners throughout the state. GIS modeling techniques can be employed to refine location of key habitat and species overlap areas.
2.1.3. How to Use the Species Accounts
Species accounts are arranged by taxonomic group and are
accessed by navigating the outline. Each
taxonomic section of the species accounts contains an overview, a list of
species for that group, links to individual species occurrence maps, a
literature cited, and a link to print all species occurrence maps
The overview sections contain information that places
Kentucky’s fauna in a national and worldwide context in addition to specifics
about Kentucky. There may also be maps,
tables, and figures relevant to that taxonomic group. A hyperlinked species list immediately
follows the overview. Clicking on a
species name will automatically display the account for that animal. The accounts cover a variety of information
about individual species such as status, trend, and habitat. Please see the Explanation of fields
in species accounts (Appendix 2.13) for a
detailed description of each field. A
link is provided within each account that allows users to view the occurrence
and range map for that species. To view all maps for a taxonomic group choose the ‘Download all
Statewide Maps’ link. This opens
a large PDF file that ranges from 4 megabytes for mammals and up to 67 megabytes
for fish. This file can be printed to
hard copy or simply viewed on-screen. To
save this file on your computer, right click on the “Download” link, and select
“Save Target As” (in Internet Explorer) or “Save Link As” (in Netscape).
If these files are too large for downloading on a particular system, a CD-ROM is available by contacting us. Species maps vary somewhat between aquatic and terrestrial groups (see map legends, Appendix 2.14). However, all available occurrence records are always displayed in one map while those acquired since 1984 are displayed separately.
2.2.1.
Fishes and Lampreys (Class Actinopterygii and
Cephalaspidomorphi) Overview
Kentucky contains one of the most diverse fish faunas in the United States, exceeded only by Alabama and Tennessee. Currently, 260 species are known to occur or have occurred within the state, representing 69 genera and 30 families. Of the 260 species, 24 (9%) are the result of either intentional or accidental introduction by human activities, and 10 (4%) are presumed extinct or extirpated from the state (Kentucky State Nature Preserves Commission 2004). Kentucky’s native fish fauna (236 species) represents approximately 30% of the entire native North American freshwater fish fauna (792 species; Lydeard and Mayden 1995). The most current list of rare and extirpated and/or extinct species maintained by the Kentucky State Nature Preserves Commission (2004) includes 27 species (10%) with a conservation status of endangered, 11 (4%) that are threatened, and 16 (6%) that are of special concern. Four species (pallid sturgeon, Scaphirhynchus albus; palezone shiner, Notropis albizonatus; relict darter, Etheostoma chienense; and duskytail darter, E. percnurum) are listed by the U.S. Fish and Wildlife Service as endangered, one (blackside dace, Phoxinus cumberlandensis) is threatened, and one (Cumberland Johnny darter, Etheostoma susanae) is a candidate proposed for listing. At least 6 species (one minnow, one madtom, and four darters) are either undescribed or recognized as distinct taxa.
The only synopsis of the distribution, systematics,
habitat, and conservation status of Kentucky fishes to date is provided in Burr
and Warren (1986). Since this
publication, collecting activities in the state have revealed new information
on distribution and conservation status for many species. Accumulation of this information over the
past 20 years has been maintained primarily in the Natural Heritage Program
database of the Kentucky State Nature Preserves Commission, Kentucky Division
of Water Quality, and Kentucky Department of Fish and Wildlife Resources. The Southern Illinois University at Carbondale
(SIUC) ichthyological collection has served as the
primary depository for fish collections made in Kentucky.
The Cumberland River drainage supports the most diverse and
unusual fish fauna in Kentucky. Although
the majority of the river basin drains Tennessee, a total of 158 species occur
or once occurred in the Kentucky portion of the drainage (Burr and Warren
1986). Among these species, five darters
(smallscale darter, Etheostoma
microlepidum; barcheek
darter, E. obeyense; bloodfin
darter, E. sanguifluum; Cumberland
Johnny darter, E. susanae; and striped darter,
E. virgatum) and one minnow (blackside dace, Phoxinus
cumberlandensis) are endemic to the Cumberland
River drainage and are found in Kentucky.
Two darter species (emerald darter, Etheostoma
baileyi and arrow darter, E. sagitta) are shared
exclusively with the Kentucky River drainage.
In the upper Cumberland River drainage, the South Fork Cumberland River
drainage harbors three species (palezone shiner, Notropis albizonatus;
blackside dace, Phoxinus
cumberlandensis; and duskytail
darter, Etheostoma percnurum)
that are listed as either threatened or endangered by the U.S. Fish and
Wildlife Service.
The Green River drainage encompasses the largest area of
any river drainage in the state. It
drains multiple physiographic regions and supports a fish fauna composed of
upland and lowland species (Burr and Warren 1986). With 150 species, it ranks second to the
Cumberland River drainage in Kentucky with respect to species diversity and
endemism (Butler et al. 2003). Five
darter species (teardrop darter, Etheostoma
barbouri; splendid darter, E. barrenense; orangefin darter,
E. bellum; Kentucky darter, E. rafinesquei;
and Shawnee darter, E. tecumsehi) and one
sucker species (blackfin sucker, Thoburnia
atripinnis) are endemic to the upper Green River
drainage, and one darter species (frecklebelly
darter, Percina stictogaster)
is shared exclusively with the Kentucky River (Burr and Page, 1986; Ceas and Page, 1997).
Three species in the cavefish family Amblyopsidae
also occur in the karst region of the Green
River. At least twenty of the 61 species
listed as special concern, rare, or endangered by the Kentucky State Nature
Preserves Commission (2004) are found in the Green River drainage.
Although considerably smaller in size and species richness,
Terrapin Creek, Running Slough, and oxbows of the Mississippi River in western
Kentucky are of considerable importance in harboring several species otherwise
unknown from the state (Burr and Warren 1986).
Terrapin Creek, the only sizeable tributary of the Obion River in
Kentucky, supports six species (blacktail redhorse, Moxostoma poecilurum; least madtom, Noturus hildebrandi;
brown madtom, Noturus
phaeus; gulf darter, Etheostoma
swaini; brighteye
darter, E. lynceum; and firebelly
darter, Etheostoma pyrrhogaster)
that are unique in the state. Several
other species having limited distributions within the state maintain viable
populations in Terrapin Creek, Running Slough, and other oxbow and wetland
habitats along the Mississippi and lower Ohio Rivers (Burr and Warren 1986).
Modifications
of natural habitats are occurring at an ever-increasing rate and have had
severe impacts to Kentucky’s fish fauna.
Collection data accumulated over the past 50 years reveal that many
species are either extirpated, less abundant, or have more restricted ranges
than formerly. Activities having the
most significant impacts on aquatic habitats in the state include increased siltation and turbidity; acid drainage from coal mines;
stream dredging and channelization; drainage and
filling of swamps, oxbow lakes, and other wetlands; disposal of oil-field
brines and associated wastes; industrial and domestic pollution; widespread use
of herbicides and pesticides; and construction of impoundments. More recently, introduced species (e.g.,
Asian carps) and over-harvest of fishes have resulted in population declines
for some species (Burr and Warren 1986).
Using the
most current and available information on conservation status, distribution and
biology, as well as recommendations provided by taxonomic authorities, 59 fish
species were identified as “species of greatest conservation need” (SGCN). Most of these species were adopted from the
Kentucky State Nature Preserves Commission and U.S. Fish and Wildlife Service
threatened and endangered species lists.
Other criteria used to select SGCN species include level of endemism,
knowledge of population status, distribution, and life history characteristics,
and importance as hosts to rare or declining mussel species.
2.2.2.
Fishes and Lampreys (Class Actinopterygii and Cephalaspidomorphi) Species Accounts
2.2.3.
Mussels (Class Bivalvia) Overview
Freshwater mussels are the most at-risk group of animals in
North America. Of the 297 native mussel
species in the United States (Appendix
2.8), 71.7% are considered endangered, threatened, or of special concern,
including 21 mussels that are endangered and presumed extinct (Williams et al.
1993). Seventy species (23.6%) are
considered to have stable populations, although information is lacking for many
of these species. In 2005, seventy U.S. mussel
species were listed as federally endangered.
Mussel and their host fish populations are projected to decline if
habitats are not restored and individual species’ numbers are not increased.
The extinction and decline of mussels can be attributed to biological
and ecological requirements that make particular species more vulnerable to
human-caused effects. Habitat loss and
degraded water quality, impoundments, commercial harvest, mining, channel
degradation, exotic species, chemical non-point and point source pollutants,
and many other factors have contributed to the downward spiral of mussel
populations. Additional issues that have
contributed to mussel declines include sedimentation from agricultural land, logging
and mining operations, construction projects, stream channelization
and dredging, toxic spills and resulting fish kills, and invasion from exotic
species (Parmalee and Bogan
1998).
With the low numbers of mussels and continuing population declines, protecting
each stage in the life cycle of mussels (Appendix 2.9) becomes
critical. Life history stages include
the production of larvae (currently inhibited by few numbers of adults), host fish
attachment and development, and juvenile survival. Suitable hosts must be present and occur in
adequate numbers to increase the chance of glochidial
attachment. Good water quality and
sufficient habitat is critical to all stages of development, especially for the
larval and juvenile stages.
Kentucky has one of the most diverse mussel populations in
North America with 41 genera and 103 recognized species. Twelve mussels are presumed extinct, and 22
species are listed by the U.S. Fish and Wildlife Service as endangered (at
least 8 of the 22 are considered extirpated from the state) (Appendix 2.10, data adapted
from Williams et al. 1993, Cicerello et al. 1991).
Diverse mussel and fish populations occur in many of the
state’s river systems (Appendix
2.11). The Ohio River drainage has
historically been an important area for mussel diversity (Williams and Schuster
1989). Its tributaries now support some
of the last few strongholds of rare and endangered mussels.
Kentucky has identified 46 mussels (44.6% of 103) that are
considered to be the species of greatest conservation need. These include 19 species listed as federally
endangered, and 2 candidate species for federal listing. The states heritage program lists 25 of the
46 species (54%) as state endangered, 5 (11%) as state threatened, and 5 (11%)
as extirpated from Kentucky. Within the
46 species of greatest conservation need, there are 20 species listed as
globally rare (G1) and 25 species as rare (S1) within Kentucky (Appendix
2.3, Appendix
2.5). Kentucky has within its
boundaries some of the best populations of mussels, including the endangered fanshell, Cyprogenia stegaria, which is found in three river systems in the
state. Some of the states most diverse
populations of mussels are found in the Green River and tributaries to the
Upper Cumberland River. It is not
uncommon to find over 25-30 species and several thousand individuals at a
single site in Kentucky.
2.2.4.
Mussels (Class Bivalvia) Species Accounts
2.3. TERRESTRIAL SPECIES ACCOUNTS
2.3.1.
Amphibians (Class Amphibia) Overview
All Amphibians. The amphibians (Class Amphibia) form a moderately diverse group consisting of about 4,100 species worldwide (Conant and Collins 1991), including more that 3,700 species of frogs and nearly 400 salamanders. At the present time, 55 species are known to occur in Kentucky: 20 frogs and 35 salamanders. About 20% of these (six frogs and five salamanders) are currently tracked by the Kentucky State Nature Preserves Commission (KSNPC), and 40% of the Kentucky fauna (eight frogs and 14 salamanders) (see Appendix 2.1) was selected for inclusion into our CWCS for various conservation reasons. The most recent comprehensive treatment dealing with Kentucky’s amphibian fauna is that of Barbour (1971), but much of the information contained there is sketchy and/or out of date. The most reliable sources that are currently available include Petranka (1998) for salamanders and Conant and Collins (1991) and Minton (2001) for all amphibians.
Kentucky’s amphibians occur in a wide variety of
habitats. Some species are largely or
totally terrestrial, while others are entirely aquatic throughout their life
cycle. Some are found only in swamps
and/or bottomland forests bordering the Mississippi River and lower Ohio River,
while others prefer upland forests in various sections of the state or even the
high elevation northern hardwood forests in extreme southeastern Kentucky;
still others prefer open grasslands and prairie remnants.
All of Kentucky’s 20 frog species breed in water. Some species prefer temporary ponds, road
ruts, and ditches as breeding sites while others use permanent ponds or even
the backwater areas of rivers and large streams. Kentucky’s 35 salamander species are more
variable in breeding habitat; ten of our salamanders are completely terrestrial
at all life stages while the remaining 25 species have aquatic larvae. The terrestrial forms—which include all
Kentucky members of the genera Aneides and Plethodon—deposit their eggs in moist places on
land; the eggs are brooded by the females and all larval development takes
place within the eggs. Those species
with aquatic larval stages are themselves quite variable;seven
salamanders (Ambystoma opacum,
Desmognathus spp., Hemidactylium scutatum)
lay their eggs near water and the larvae become aquatic after hatching, while
the others actually deposit eggs in water.
Altogether, nine of Kentucky’s salamanders with aquatic larvae breed in
ponds, two use swamps and/or wetlands, two utilize large streams and rivers,
and 12 reproduce in springs, seeps, and headwater streams. All species of salamanders and frogs in
Kentucky are predaceous as adults. All
salamander larvae are also predaceous, but frog larvae (tadpoles) are
herbivores.
Frogs. Of the 20 species of frogs native to Kentucky, eight species (40% of the total fauna) were selected as species with greatest conservation need (SGCN) for inclusion in the CWCS process. Six of these (barking treefrog, bird-voiced treefrog, gray treefrog, green treefrog, northern crawfish frog, and northern leopard frog) are also listed as “special concern” by KSNPC.
We have
included two other species of frogs (southern leopard frog, wood frog) as SGCN
species on the basis of vulnerability to extirpation from Kentucky (i.e.,
isolated populations located in rapidly developing areas). Southern leopard frogs in northeastern
Kentucky seem to represent an isolated relict population that may be
genetically distinct. Wood frogs in
Fayette County along the Kentucky River Palisades are also quite isolated. Elsewhere in Kentucky, the southern leopard
frog is primarily a species of wetlands and other bottomland habitats in
central and western Kentucky, breeding most frequently in lowland ponds, while
the wood frog is most common in forested upland habitats in eastern and
southern Kentucky and breeds in ponds located in upland forests. Both the southern leopard frog and the wood
frog can thus also be considered as representative species for large amphibian
communities associated with various habitat types.
Salamanders. Of Kentucky’s 35 species of native salamanders, 14 species (40% of the total fauna) were selected for inclusion in our CWCS. Five (14%) are also listed as either endangered (two), threatened (one), or special concern (two) by KSNPC (eastern hellbender, northern redback salamander, three-lined salamander, three-toed amphiuma, and Wehrle’s salamander).
We have
included nine other species of salamanders as SGCN species as follows: the
Black Mountain salamander, Cumberland Plateau salamander, and streamside
salamander are nearly endemic to Kentucky; the Allegheny Mountain salamander
(cold dripping seeps) and the green salamander (crevices in shaded sandstone
cliffs) are habitat specialists that occur primarily in eastern Kentucky; the
four-toed salamander and the mole salamander are uncommon pond-breeding species
that occur in both upland and lowland forests; the western lesser siren is
primarily a wetland species; and the southern zigzag salamander is included for
biogeographic reasons. Several SGCN species, including the Allegheny
Mountain salamander, Black Mountain salamander, Cumberland Plateau salamander,
green salamander, and some of their close relatives (i.e., northern dusky
salamander, northern slimy salamander) appear to be declining or disappearing
from large portions of their ranges both in Kentucky and elsewhere; this merits
further investigation and better documentation.
2.3.2.
Amphibians (Class Amphibia) Species Accounts
2.3.3. Birds (Class
Aves) Overview
Kentucky is an ecoregionally
diverse state that transitions from alluvial and coastal plain soils, to a
northern hardwood forest landscape, and to the mountains of the Cumberland
Plateau. The Ohio and Mississippi Rivers
form Kentucky’s northern and western borders, respectively. Other major river systems include the
Tennessee and Cumberland rivers that form the Land Between the Lakes (LBL)
area. Kentucky is rich in floodplain
forest, upland forest, high elevation forest, grassland, riverine,
and marsh habitats. Because of this
diversity, Kentucky falls within four Bird Conservation Regions (BCR) under the
North American Bird Conservation Initiative (NABCI). These include the following: Central
Hardwoods (BCR 24) which includes most of the state; the Appalachian Mountains
(BCR 28) which includes the Cumberland Mountains and Plateau; the Mississippi
Alluvial Valley (BCR 26) which covers a small portion of the Jackson Purchase
along the Mississippi River; and the Southeastern Coastal Plain (BCR 27) which
covers most of the Jackson Purchase west of Land Between the Lakes ( Appendix
2.12 ). BCR 27 is currently in the process of being
split into the East Gulf Coastal Plain sub-BCR.
Approximately 375 species of birds have been recorded in
Kentucky, and of these, about 150 species regularly breed in the state (B.
Palmer-Ball, pers. comm.). Taxonomically, these species can be
categorized as landbirds, waterbirds,
shorebirds, and waterfowl. Continental
or range wide bird conservation plans have been created to cover individual or
suites of species and include the Partners In Flight’s (PIF) North American Landbird Conservation Plan (NALCP; Rich et al. 2004), the
United States Shorebird Conservation Plan (USSCP; Brown et al. 2001), the North
American Waterbird Conservation Plan (NAWCP; Kushlan et al. 2002), the North American Waterfowl
Management Plan (NAWMP; Plan Committee 2004), and the Northern Bobwhite Conservation Initiative
(NBCI; Dimmick et al. 2002). Where possible, Kentucky’s CWCS follows
recommendations highlighted under these continental plans and includes 81
species (Appendix 1.1). Of the 81
species, four have been extirpated as breeding birds from Kentucky: greater
prairie-chicken, red-cockaded woodpecker, swallow-tailed kite, and black tern,
although the black tern still occurs in the state as a transient. Three federally listed species (interior
least tern, whooping crane, and bald eagle) are also included in Kentucky’s
CWCS.
Landbirds. Kentucky falls under four PIF physiographic regions. These include the Appalachian Mountains, the Interior Low Plateaus, the Mississippi Alluvial Valley, and the East Gulf Coastal Plain. Maps of the physiographic regions as well as conceptual conservation plans for each region are available at the PIF website ( http://www.blm.gov/wildlife/pifplans.htm ). Avian species selected for inclusion in the CWCS were based on Kentucky’s heritage list (which is based solely on breeding birds) [Kentucky State Nature Preserves Commission 2004], the NALCP, physiographic region PIF plans, USFWS Watchlist for Region 4 states (Hunter 2004), and the Central Hardwoods Venture Concept Plan (Fitzgerald et al. 2003) and includes 46 landbird species (Appendix 1.1).
Waterfowl. The North American Waterfowl Management Plan predates NABCI
and, as such, planning units are based on joint ventures (JV) rather than BCRs. Kentucky falls
within two JVs: the Lower Mississippi Valley JV (which covers BCRs 26 and 27 in Kentucky as well as part of BCR 24) and
the Central Hardwoods JV (which covers all of BCR 24). Updates to the NAWMP and maps of the JVs can
be found on the USFWS website (http://www.fws.gov/birdhabitat/nawmp/nawmphp.htm). Three species of waterfowl are included in
the CWCS and are based on Kentucky’s Heritage list (Kentucky State Nature
Preserves Commission 2004), the NAWMP (Plan Committee 2004), and the Central
Hardwoods Venture Concept Plan (Fitzgerald et al. 2003) (Appendix
1.1).
Waterbirds. Waterbirds are a diverse group of species that includes gulls, terns,
pelicans, wading birds, and marsh birds.
As one of the newest initiatives, the North American Waterbird
Conservation Plan sets fourth a plan for conserving waterbirds
and is in the process of evaluating the population status of 210 species of waterbirds that range in North and Central America. Waterbird planning
regions have been established and Kentucky falls within two of these regions:
the Upper Mississippi Valley/Great Lakes and the Southeast U.S. planning
regions. Maps of the planning regions
and version 1 of the plan are available at the Waterbird
Conservation for the America’s website (http://www.waterbirdconservation.org/). Eighteen species of waterbirds
were selected for inclusion in Kentucky’s CWCS based on Kentucky’s heritage
list (breeding birds) [Kentucky State Nature Preserves Commission 2004], the
USFWS Watchlist for Region 4 states (Hunter 2004),
the Central Hardwoods Venture Concept Plan (Fitzgerald et al. 2003), and
version 1 of the NAWCP (Kushlan et al. 2002) (Appendix
1.1).
2.3.4.
Birds (Class Aves) Species Accounts
2.3.5. Mammals
(Class Mammalia) Overview
The Class Mammalia includes
>4,600 species worldwide, a fairly low diversity when compared to most other
Classes in Kingdom Animalia (Whitaker and Hamilton
1998). However, mammals are distributed
nearly worldwide, being found in every ocean and on every continent except Antartica (Whitaker and Hamilton 1998). According to Kays
and Wilson (2002), North America (north of Mexico) is home to 442 species of
mammals. The eastern United States (i.e.,
east of the Mississippi River) supports populations of approximately 121
species of mammals, most of which are native, although some are exotic or
domestic animals that have become established (Whitaker and Hamilton 1998).
Kentucky offers a diversity of habitat types across the
state, along with numerous topographies, soils, and water sources (i.e.,
streams, rivers, ponds, sloughs, lakes, and reservoirs). For example, elevations range from 1,262 m in
the rugged mountains of southeastern Kentucky to 78 m in the Mississippi River
floodplains of western Kentucky, with extremely variable types of topography
and thousands of kilometers of streams in between (Jones 2005). Highly diverse plant communities occur
throughout the state in accordance with each ecoregion
because of changes in soil properties, soil moisture, and slope characteristics
(Jones 2005). The variability in habitat
types throughout Kentucky supports an interesting diversity of mammals, a
diversity that encompasses mammal communities typical of the region as well as
species typically found elsewhere. As
examples, several animals (e.g., Rafinesque’s
big-eared bat, Corynorhinus rafinesquii; swamp rabbit, Sylvilagus
aquaticus) reach their northern limits in or just
north of Kentucky, others (e.g., cotton mouse, Peromyscus
gossypinus) are typical of southern states,
western states (e.g., prairie vole, Microtus
ochrogaster; coyote, Canis
latrans), northern states (e.g., meadow jumping
mouse, Zapus hudsonius),
or even the Appalachian Mountains (e.g., Appalachian cottontail, Sylvilagus obscurus;
rock shrew, Sorex dispar)
(Barbour and Davis 1974, although their taxonomy differed on several species).
Mammal diversity in Kentucky has been described to varying
extents. Barbour and Davis (1974) discussed
64 species of mammals in their compilation of data on Kentucky’s mammals. They only included species with recent
records (i.e., not extirpated species like elk [Cervus
elaphus] or American bison [Bos
bison]), and taxonomy they used differed from what it is now accepted,
thereby not recognizing a couple of species.
Choate et al. (1994) listed 67 species for Kentucky, but included
several species that have been extirpated for decades (e.g., gray and red
wolves, Canis lupus and C. rufus, respectively; fisher, Martes
pennati; mountain lion, Felis
concolor; American bison) or species they had no
records for but assumed should be present (e.g., rock vole, Microtus
chrotorrhinus; porcupine, Erethizon
dorsatum).
In the latter category, Choate et al. (1994) did not include rock shrew,
nine-banded armadillo (Dasypus novemcinctus), pygmy shrew (Sorex
hoyi), or least weasel (Mustela
nivalis), species that have recently (within the
last 10 years) been recorded in Kentucky.
Diversity
within the mammal group is particularly high in Kentucky with regard to
bats. Kentucky provides habitat for 14
species of bats, three of which are federally endangered: Indiana bat (Myotis sodalis),
gray bat (Myotis grisescens),
and Virginia big-eared bat (Corynorhinus townsendii virginianus). In the south-central United States, there are
only 17 species of wide-ranging bats (Choate et al. 1994), and even one of
those (Brazilian free-tailed bat, Tadarida brasiliensis) is an “accidental wanderer” into Kentucky
(Barbour and Davis 1974). In addition to
the variety of terrestrial habitats available to bats in Kentucky (e.g., upland
forests, riparian corridors, forested wetlands, etc.), subterranean Karst caves and sinkholes are numerous, and scattered
throughout the state. These caves and
sinkholes offer breeding sites for gray bats and Virginia big-eared bats, but
also provide important hibernacula for numerous species of bats that migrate
from other states in the region.
Unfortunately, disturbance and harassment of bats in caves has been a
major factor and likely has contributed to decline in many species.
Although it appears that a wealth of knowledge on
Kentucky’s mammal community exists, there is still much to learn. Studies within the last decade funded solely
or in part by Kentucky Department of Fish and Wildlife Resources have expanded
our knowledge about many species of mammals.
A longer-term statewide small mammal survey provided us distribution and
abundance information on 29 species, many of which we knew very little. Concerted survey efforts for Appalachian
cottontails showed the species was not isolated solely to the most rugged
portions of southeastern Kentucky, but instead was found throughout much of
eastern Kentucky and even extended into the “Knobs” portion of central Kentucky. Trapping efforts for American black bears (Ursus americanus)
and Allegheny woodrats (Neotoma
magister) have provided valuable population and
distribution information for these species.
Despite all of the information these projects have provided us, there is
still a wealth of information to be gained.
Overall, we have a very poor understanding of the effects of land use
practices on mammal communities, and most importantly, population status of
most mammal species in Kentucky. Through
our strategy, we hope to initiate numerous research and survey projects to help
answer the questions we have about mammal diversity and abundance in Kentucky,
especially as it pertains to our priority mammal species (see Appendix 3.2).
2.3.6. Mammals (Class Mammalia)
Species Accounts
2.3.7. Reptiles (Class
Reptilia) Overview
The reptiles (Class Reptilia)
include about 6,300 species worldwide (Conant and
Collins 1991); the largest subgroups are the lizards (about 3,700) and the
snakes (about 2,300) species. The
turtles (more than 240 species) are included with the reptiles here, but recent
studies have shown that these animals are distinct from all other reptiles and form
a separate class. At the present time,
56 species of reptiles are known to occur in Kentucky (9 lizards, 33 snakes,
and 14 turtles). The most recent
comprehensive treatment dealing with Kentucky’s reptile fauna is that of
Barbour (1971), but much of the information contained there is unclear and/or
out of date. The most reliable sources
that are currently available include Ernst et al. 1994 for turtles, Ernst and
Ernst (2003) and Meade (2005) for snakes, and Conant
and Collins (1991) and Minton (2001) for all reptiles. Aside from these widely available published
materials, much additional information on Kentucky’s reptiles and amphibians
has been pulled from a variety of less well-known sources (e.g., university and
museum collections, unpublished reports, theses, dissertations, journal articles,
and biologists’ observations and field notes) and entered into databases that
are being used to track species occurrences and population trends, create
up-to-date species distribution maps, and compile state-specific life history
information for the ongoing revision of Amphibians and Reptiles of Kentucky
(J.R. MacGregor, in progress).
The most significant of these include: (1) the comprehensive
herpetological data base that is being developed and maintained by the
biological staff at East Kentucky Power Cooperative (EKPC); (2) the amphibian
and reptile sections of the Kentucky Natural Heritage database housed at
Kentucky State Nature Preserves Commission (KSNPC); and (3) the Kentucky Fish
and Wildlife Information System (KFWIS) database housed at KDFWR.
Eighteen reptile species (32% of the Kentucky fauna
including three lizards, 12 snakes, and three turtles) are currently tracked by
KSNPC; 27 species (four lizards, 17 snakes, and six turtles) were selected for
our CWCS for various conservation reasons (see
Appendix 2.1). Most of our reptiles
are native, but at least one species (common wall-lizard) is a European exotic
that has been introduced into northern Kentucky. The eastern coachwhip,
a snake found historically in the Park City area of west-central Kentucky, has
not been seen within the state for many years and was possibly an introduced
species as well (note: we included it in our CWCS because of its’ unclear
history in the state).
Kentucky’s reptiles occur in a wide variety of
habitats. In general, the lizards tend
to prefer dry, open areas although a few species (e.g., five-lined skinks)
sometimes occur in damp woodlands as well.
The snakes form a highly variable group from a habitat perspective, but
virtually all species require some degree of openness if they are to survive in
heavily forested areas. Most Kentucky
turtles (13 of 14) are primarily aquatic and leave the water only to make
overland migrations between water bodies or to lay their eggs; only 1 species
(eastern box turtle) is terrestrial. All
of Kentucky’s lizards and snakes are carnivorous; most turtles are more
omnivorous as adults and largely carnivorous as hatchlings, but the map turtles
(genus Graptemys) feed almost completely on
invertebrates and fishes.
Lizards. Four of Kentucky’s nine lizard species (44% of the total
fauna) were selected for our CWCS. Three
of these (coal skink, southeastern five-lined skink, and eastern slender glass
lizard) are also listed as either threatened or special concern by KSNPC. The six-lined racerunner has been added here
because the lack of recent records indicates that a number of populations have
been lost and much of its habitat has essentially disappeared from the
landscape.
Snakes. Seventeen of Kentucky’s 33 species of snakes (52% of the
total fauna) were selected for our CWCS.
Eleven species (33% of the snake fauna), including the broad-banded
water snake, copperbelly water snake, corn snake,
eastern ribbon snake, Kirtland’s snake, Mississippi green water snake, northern
pine snake, scarlet kingsnake, western mud snake,
western pigmy rattlesnake, and western ribbon snake, are listed as either
endangered, threatened, or special concern by KSNPC. One additional snake (eastern coachwhip) has not been seen here since the early 1970’s
and has likely been extirpated, but there is evidence that the Kentucky
population may have originated from a now-defunct roadside reptile zoo and thus
the coachwhip may not have been native.
Five additional snakes have been added to the list due to
conservation concerns. Recent records
are very sparse for northern scarlet snakes and southeastern crowned snakes;
both species have apparently disappeared from many areas where they once could
be found with some regularity. Western
cottonmouths and diamondback water snakes seem to have declined in both range
and numbers in the coal-mining areas of western Kentucky. The timber rattlesnake appears to have stable
numbers in Kentucky but is known to be declining in numerous other states
within its range. Regular monitoring of
timber rattlesnake numbers and habitat use within Kentucky is essential so that
the rangewide status of the species can be
ascertained and consistently tracked.
Turtles. Six of Kentucky’s 14 turtles species (43% of the fauna) are
included within our CWCS. Three of
these—the alligator snapping turtle, midland smooth softshell,
and southern painted turtle—are listed as either threatened or special concern
by KSNPC. Three additional turtles
(false map turtle, Mississippi map turtle, and mud turtle) have been added as
CWCS species for conservation reasons.
The two map turtles are largely restricted to western Kentucky rivers
and are limited by the scarcity of suitable nesting habitat (natural sand
bars). Mud turtle populations in central
Kentucky occur in wetland complexes that have developed in natural sinkhole
ponds and appear to have declined seriously in recent decades as more
development has taken place within their limited ranges.
2.3.8. Reptiles (Class Reptilia) Species Accounts
Barbour, R.W., 1971. Amphibians & reptiles of Kentucky. University Press of Kentucky, Lexington, Kentucky.
Barbour, R.W., Davis, W.H.. Mammals of Kentucky. 1974. Lexington, Kentucky, University Press of Kentucky.
Brown, S., Hickey, C., Harrington, B., Gill, R.. The U.S. Shorebird Conservation Plan . 2001. Manomet, Massachusetts, Manomet Center for Conservation Sciences. Brown, S, Hickey, C., Harrington, B., and Gill, R.
Burr, B.M., L. M. Page 1986. Zoogeography of fishes of the lower Ohio-upper Mississippi Basin. Pages 287-324 in C. H. Hocutt, E. O. Wiley editors. The Zoogeography of North American Freshwater Fishes. Wiley Interscience, New York..
Burr, B.M., Warren, M.L.Jr., 1986. A Distributional Atlas of Kentucky Fishes. Volume Number 4 . Kentucky State Nature Preserves Commission Scientific and Technical Series.
Butler, R.S., Kessler, R., J. B. Harrel, 2003. Down by the Green River. U.S. Fish and Wildlife Service Endangered Species Bulletin 28:20-21.
Ceas, P.A., Page, L.M., 1997. Systematic studies of the Etheostoma spectabile complex (Percidae; subgenus Oligocephalus), with descriptions of four species. Copeia496-522.
Choate, J.R., Jones Jr., J.K., Jones, C.. Handbook of mammals of the south-central states. 1994. Baton Rouge, Louisiana, Louisiana State University Press.
Cicerello, R.R., M. L. Warren, Jr., G.A. Schuster, 1991. A distributional checklist of the freshwater unionids (Bivalvia:Unionoidea) of Kentucky. American Malacological Bulletin 8:113-129.
Conant, R., Collins J.T.. A field guide to reptiles and amphibians. Eastern and Central North America. 450 . 1991. Boston, MA, Houghton Mifflin Company.
Dimmick, R.W., Gudlin, M.J., McKenzie, F.M.. The northern bobwhite conservation initiative. 2002. South Carolina, Southeastern Association of Fish and Wildlife Agencies.
Ernst, C.H., Ernst, E.M.. Snakes of the United States and Canada. 668 pp. 2003. Washington and London, Smithsonian Books.
Ernst, C.H., Lovich J.E, Barbour, R.W.. Turtles of the United States and Canada. 578 pp. 1994. Washington and London, Smithsonian Institution Press.
Fitzgerald, J.A., Wathen, G., Howery, M.D., Lisowsky, W.P., McKenzie, D.F., Pashley, D.N.. The Central Hardwoods Joint Venture Concept Plan. 2003. Tennessee Wildlife Resources Agency.
Hunter, C.. 2004. Notes: Personal communication
Jones, R.L., 2005. Plant life of Kentucky: an illustrated guide to the vascular flora. The University Press of Kentucky, Lexington, KY.
Kays, R., Wilson, D.E., 2002. Mammals of North America. Princeton University Press, Princeton, NJ.
Kentucky State Nature Preserves Commission . Kentucky
State Nature Preserves Commission Database.
2004. Kentucky State Nature
Preserve Commission . 2004.
Notes: Data printouts
Kentucky State Nature Preserves Commission. Rare and extirpated biota of Kentucky. KSNPC. World Wide Web . 2004. November 17th, 2004.
Kushlan, J.A., Steinkamp, M.J., Parsons, K.C., Capp, J., Acosta Cruz, M., Coulter, M., Davidson, I., Dickson, L., Edelson, N., Elliot, R., Erwin, R.M., Hatch, S., Kress, S., Milko, R., Miller, S., Mills, K., Paul, R. , Phillips, R., Saliva, J.E., Sydeman, B., Trapp, J., Wheeler, J., Wohl, K.. Waterbird Conservation for the Americas: The North American Waterbird Conservation Plan. 2002. Washington, D.C., USA, Waterbird Conservation for the Americas.
Lydeard, C., R. L. Mayden, 1995. A diverse and endangered aquatic ecosystem of the southeast United States. Conservation Biology 4:800-805.
Meade, L.E.. Kentucky Snakes: Their Identification, Variation and Distribution. 322pp. 2005. Frankfort, Kentucky State Nature Preserves Commission.
Minton, S.A.. Amphibians and Reptiles of Indiana. 404 pp. 2001. Indianapolis, IN., Indiana Academy of Science.
North American Waterfowl Management Plan (NAWMP), P.C.. North American Waterfowl Management Plan 2004. Strategic Guidance: Strengthening the Biological Foundation. 2004. Canadian Wildlife Service, U.S. Fish and Wildlife Service, Secretaria de Medio Ambiente y Recursos Naturales.
Parmalee, P.W., Bogan, A.E.. The freshwater mussels of Tennessee. 1998. Knoxville, Tennessee, University of Tennessee Press.
Parmalee, P.W., Kippel, W.E., Bogan, A.E.. Notes on the prehistoric and present status of the Naiad fauna of the middle Cumberland River, Smith County, Tennessee. Nautilus 94, pages 93-105. 1980.
Petranka, J.W., 1998. Salamanders of the United States and Canada. Smithsonian Institution Press, Washington, D.C.
Rich, T.D., Beardmore, C.J., Berlanga, H., Blancher, P.J., Bradstreet, M.S.W., Butcher, G., Demarest, D.W., Dunn, E.H., Hunter, W.C., Inigo-Elias, E.E., Kennedy, J.A., Martell, A.M., Panjabi, A.O., Pashley, D.N., Rosenberg, K.V., Rustay, C.M., Wendt, J.S., Will, T.C.. Partners in Flight North American Landbird Conservation Plan. 2004. Ithaca, New York, Cornell University.
Whitaker, J.O., Hamilton Jr., W.J.. Mammals of the eastern United States. 1998. Ithaca, New York, USA and London, England, UK, Cornell University Press.
Williams, J.C., G.A. Schuster. Freshwater mussel investigations of the Ohio River. 1989. Frankfort, KY., Kentucky Department of Fish and Wildlife Resources.
Williams, J.D., Warren Jr., M.L., Cummings, K.S. ,
Harris, J.L., Neves, R.J.. Conservation Status of
Freshwater Mussels of the United States and Canada. Fisheries 18 (9), pages
6-22. 1993.