2012 SOUTHEASTERN NATURALIST 11(4):589–598
The Distribution and Habitat of Centruroides hentzi
(Banks) (Scorpiones, Buthidae) in Georgia
Dirk J. Stevenson1,*, Greg Greer2, and Matt J. Elliott3
Abstract - Field collections made by the authors in pineland ecosystems in southern Georgia
during 2011 significantly expand the previously published range limits of the scorpion
Centruroides hentzi in Georgia. We commonly found specimens beneath the exfoliating
bark of Pinus palustris (Longleaf Pine) and P. elliottii (Slash Pine) snags, stumps, and
logs in sandhills and pine flatwoods habitats, documenting this scorpion from 50 sites in
34 south Georgia counties, and extending the known range of C. hentzi 150 km north (from
near Waycross, Ware County, GA) to Statesboro, Bulloch County, GA. Our collections
indicate that the species is widespread in pine-dominated uplands throughout much of
the lower and middle Coastal Plain of southern Georgia. We comment on the life history,
ecology, and habitat requirements of the species based on this survey and the existing literature.
In Georgia, C. hentzi is a characteristic associate of Longleaf Pine and Slash Pine
ecosystems, is often locally abundant, and is part of an arthropod–vertebrate food web that
includes the endangered Picoides borealis (Red-cockaded Woodpecker).
Scorpion diversity in the eastern United States is notably low, with only 5
species occurring east of the Mississippi River (Shelley and Sissom 1995). Only
2 species are native to Georgia: Vaejovis carolinianus Beauvois (Vaejovidae)
and Centruroides hentzi Banks (Buthidae) (Shelley and Sissom 1995). Vaejovis
carolinianus (to 50 mm in length) is an upland species mostly restricted to the
Piedmont, Ridge and Valley, and Mountain provinces; its overall range extends
north and west of the Fall Line as far north as the Ohio River in central Kentucky
(Gibbons et al. 1990, Shelley 1994). Although superficially similar to C. hentzi
and sometimes found in pine-dominated landscapes, V. carolinianus has never
been recorded from the Coastal Plain of Georgia or found sympatric with
C. hentzi. The comparatively slender C. hentzi (Fig. 1), also small to medium
sized (to 60 mm in length), is brown with yellowish stripes and appendages. Like
other Centruroides species, adults exhibit sexual dimorphism, with males having
lean bodies and elongated metastomal segments (Polis and Sissom 1990, Stahnke
and Calos 1977). Stings to humans by C. hentzi and V. carolinianus are painful,
but do not have lasting effects or serious medical consequence (D.J. Stevenson,
G. Greer, and M.J. Elliot, pers. observ.; Muma 1967).
Prior to our study, the known distribution of C. hentzi included most of
Florida, extreme southwestern Alabama, and extreme southern Georgia (Shelley
1The Orianne Society, 414 Club Drive, Hinesville, GA 31313. 2Greg Greer Enterprises,
Inc., 1469 Bollingbrook Road, Marietta, GA 30067. 3Georgia Department of Natural Resources
Nongame Conservation Section, 2065 US Highway 278 SE, Social Circle, GA
30025. *Corresponding author - firstname.lastname@example.org.
590 Southeastern Naturalist Vol. 11, No. 4
and Sissom 1995). Centruroides hentzi was not formally reported from Georgia
until 1995, when Shelley and Sissom (1995) mapped a number of records for
the southern-most tier of Georgia counties (i.e., those counties contiguous with
the Florida state line); localities published in their article included one Georgia
barrier island (Cumberland Island). Shelley and Sissom (1995) treated C. hentzi
records from urban areas well outside the perceived range as accidental human
importations, including sites in Georgia (Harris and Muscogee counties),
North Carolina (Brunswick, Carteret, and Durham counties), and South Carolina
From previous field experience, we knew that: 1) C. hentzi was in fact much
more widely distributed in Georgia than reflected by Shelley and Sissom (1995),
the absence of museum specimens notwithstanding; 2) where populations occur,
C. hentzi can be predictably found in pine-dominated habitats (especially sandhills
and pine flatwoods) by peeling exfoliating bark from pine snags, stumps,
During 2011, we conducted diurnal surveys for C. hentzi at sites located
throughout southern Georgia, with an emphasis on that portion of the Coastal
Plain north of the C. hentzi localities mapped in Shelley and Sissom (1995). Our
primary focus during these field surveys was to document C. hentzi from as many
sites as possible, while sampling as far north in the Coastal Plain of Georgia as
the presence of potentially suitable Pinus palustris Miller (Longleaf Pine) and
Figure 1. An adult Centruroides hentzi from Atkinson County, GA. Photo by Greg Greer.
2012 D.J. Stevenson, G. Greer, and M.J. Elliott 591
P. elliottii Engelmann (Slash Pine) sandhills and pine flatwoods allowed. Although
we often flipped surface cover objects (logs, pieces of bark, trash, boards,
etc.) resting directly on the ground, our primary survey method was peeling the
exfoliating bark from pine snags, stumps and logs—especially Longleaf Pine and
Slash Pine, and occasionally P. taeda L. (Loblolly Pine). Late in our survey, we
also searched for scorpions under the sloughing bark scales of living pines. Based
on soil type and dominant vegetation (NatureServe 2011, Wharton 1978), we
classified habitat type at each survey site as either “sandhill” or “pine flatwoods”
(or in the case of barrier island sites, “maritime forest”). Sandhill habitats are
xeric communities underlain by well-drained to excessively well-drained deep
sandy soils; patches of bare sand and vegetation adapted to droughty conditions
(e.g., Longleaf Pine, Quercus laevis Walter [Turkey Oak], Yucca filamentosa
L. [Bear-grass]) characterize these habitats. Pine flatwoods (open, “savannahlike”
woodlands) are mesic habitats occurring on acidic sandy soils; an organic
hardpan layer located 46–60 cm beneath the ground surface causes soils to be
saturated during wet periods. Longleaf and/or Slash Pine dominate the canopy,
with common shrubs including Myrica cerifera L. (Wax Myrtle) and Ilex glabra
Gray (Gallberry); a luxuriant and extremely diverse ground cover of grasses,
sedges, and herbs including Aristida stricta Michaux (Wiregrass) is characteristic
of frequently burned, high-quality examples of mesic pine flatwo ods.
Specimens were captured with forceps, preserved in 75% ethanol, and deposited
in the arthropod collection at the Georgia Museum of Natural History
(GMNH) in Athens. We made inquiries with curators at the following museum
collections in an effort to locate specimens of C. hentzi collected post-1990 in
Georgia so that we might learn of recent records not reported by Shelley and Sissom
(1995): Archbold Biological Station, Venus, FL; Auburn University, Auburn,
AL; Clemson University, Clemson, SC; Florida State Collection of Arthropods,
Gainesville, FL; Georgia Southern University (GSU), Statesboro, GA; GMNH,
Athens, GA; Mississippi Entomological Museum, Mississippi State , MS.
Results and Discussion
In 2011, we collected 128 specimens of C. hentzi at 50 sites in 34 Georgia
counties (Fig. 2). Shelley and Sissom (1995) reported C. hentzi from only 3 of
these counties: Charlton, Clinch, and Ware (Fig. 2). At 32 (64.0%) of our collection
sites, we classified habitat type as sandhill (this total included 10 sites that
were highly disturbed or pine plantations); at 16 (32.0%) of our collection sites,
we classified habitat type as pine flatwoods (including 8 sites that were disturbed
or pine plantations); and at 2 (4.0%) of our collection sites, we classified habitat
type as maritime forest (including 1 site that was disturbed). Microhabitat for our
scorpion collections included: under log (n = 1 specimen, 0.8%); under bark of
Longleaf Pine snag/stump/log (n = 49, 38.3%); under bark of Slash Pine snag/
stump (n = 26, 20.3%); under bark of Loblolly Pine snag/stump (n = 4, 3.1%); under
bark of unidentified pine snag/stump/log (n = 22, 17.2%); and under flaking
592 Southeastern Naturalist Vol. 11, No. 4
bark scales of living Slash Pine (n = 26, 20.3%). Our search of major museum
holdings for recent (1990–present) C. hentzi records from Georgia located records
from one site each in Bulloch and Toombs counties (GSU) and Camden and
Miller counties (GMNH) (Fig. 2). New Centruroides hentzi localities for Georgia
are compiled in Appendix 1.
Our C. hentzi records demonstrate that C. hentzi is common in sandhill
and pine flatwoods environments and is essentially continuously distributed
throughout much of the lower and middle Coastal Plain of southern Georgia.
Furthermore, our records indicate that C. hentzi occurs widely in the Dougherty
Plain, Tifton Uplands, and the recently exposed (Plio-Pleistocene) Coastal Plain
Marine Flatlands physiographic provinces (Wharton 1978). Georgia barrier island
records include Jekyll Island, Little Cumberland Island, St. Simon’s Island
(this study), and Cumberland Island (Shelley and Sissom 1995); additionally, we
received a credible report of C. hentzi for Sapelo Island (W. Dopson, Brunswick,
GA, pers. comm.). Our scorpion collections from Jekyll Island and St. Simon’s
Island were from upland maritime habitats forested with large scattered Slash
Pines, Quercus virginiana Miller (Live Oak), Juniperus virginiana L. (Eastern
Figure 2. Distribution of Centruroides hentzi in Georgia.
2012 D.J. Stevenson, G. Greer, and M.J. Elliott 593
Red Cedar), and Sabal palmetto (Walter) (Cabbage Palm); Serenoa repens
Bartram (Saw Palmetto) was common in the shrub layer. At Jekyll Island, we
collected several C. hentzi from a pine snag at the edge of a brackish marsh.
The northern-most locality (Statesboro, Bulloch County, GA) reported in this
article is ca. 150 km north of the northern-most record previously published for
the species (Shelley and Sissom 1995). Records for Statesboro include a specimen
collected in 2009 from pineland habitat (since destroyed) located on the
Georgia Southern University campus (L. Durden, Statesboro, GA, pers. comm.).
Our repeated efforts to document C. hentzi farther north in Georgia were unsuccessful,
even at seemingly optimal sites like the Fall Line Sandhills (Talbot and
Taylor counties), Ohoopee Dunes (Emanuel County), and sandhills near the Savannah
River at Yuchi Wildlife Management Area (Burke County).
At many sites where we documented C. hentzi, we found scorpions within
only a few minutes of searching, often finding five or more specimens in the
same pine snag. In November–December, we found large numbers of C. hentzi
of various size classes under and within layers of flaking bark scales at the base
of large, living Slash Pines. We collected C. hentzi during all months of the year
except June and September. In summer 2011, southern Georgia experienced a
period of extended hot temperatures and a protracted drought, which may explain
our difficulty in locating specimens at this time.
Centruroides hentzi occurs in a region where freezing temperatures are sometimes
experienced, and temperature may be a factor limiting the northern extent
of the species’ range. We suspect that individuals insulate themselves during
cold weather by retreating into the interiors of snags/logs, or hiding deep beneath
overlapping plates of exfoliating bark. Whitmore et al. (1985) discovered that a
freeze-tolerant congener, Centruroides vittatus (Say), a species that ranges north
to southern Missouri (Shelley and Sissom 1995), survives freezing temperatures
by ice-nucleating activity (wherein potent ice-nucleating activity compartmentalized
in the gut induced ice formation). There are numerous other Coastal Plain
species (e.g., Saw Palmetto and Drymarchon couperi Holbrook [Eastern Indigo
Snake]) that are widely distributed in the Coastal Plain of Georgia, but do not
range north to the Fall Line (Diemer and Speake 1983, McNab 198 0).
Little has been published relating to the life history and ecology of
C. hentzi. Predators include the federally endangered Picoides borealis Vieillot
(Red-cockaded Woodpecker) (Hanula and Engstrom 2000; J. Macey, Fort
Stewart, GA, pers. comm.) and a large non-native anuran, Osteopilus septentrionalis
Dumeril and Bibron (Cuban Treefrog) (Granatosky et al. 2011).
Biologists monitoring Red-cockaded Woodpecker populations commonly encounter
specimens of C. hentzi 2–12 m off the ground while scaling bark from
living, mature Longleaf and Slash Pines as part of tree banding and artificial
cavity installation (L. Carlile, Fort Stewart, GA, pers. comm.). Also of note,
pitfall and funnel traps associated with terrestrial drift-fence arrays captured
numerous C. hentzi from spring though autumn on both Fort Stewart, GA (in
sandhill and pine flatwoods habitats; D. Stevenson, unpubl. data) and on Eglin
594 Southeastern Naturalist Vol. 11, No. 4
Air Force Base, FL (in sandhill habitats; D. Steen, Auburn University, Auburn,
AL, unpubl. data), indicating that the species is not solely arboreal and
frequently prowls overland, probably at night. Centruroides hentzi, like numerous
other buthid species, may aptly be described as a non-burrowing errant
scorpion because it does not dig a resident burrow and may be active both on
the ground and on vegetation (McReynolds 2008).
Folkerts et al. (1993) include C. hentzi among their list of arthropods associated
with xeric Longleaf Pine habitats in the southeastern US, mentioning
that it is commonly encountered in Longleaf Pine habitats in Florida. Muma
(1967) stated that C. hentzi occurs under litter, logs, stones, and under the
bark of dead trees in Florida. Specimens reported in his paper included scorpions
found beneath pine bark of snags and logs up to 7 m above the ground.
Although our study did not quantitatively examine habitat characteristics of
those sites where we found C. hentzi in Georgia, it was apparent from the collections
reported herein, and from the previous experience of the authors, that
C. hentzi frequents open-canopied, sunlit situations; a grassy or Saw Palmetto
ground cover and exposed bare mineral soil lacking a heavy accumulation of
leaf litter or pine needle litter typifies habitats supporting this scorpion. Additionally,
with respect to microhabitat, it is clear that C. hentzi is strongly tied
to pine bark on both living and dead trees, especially Longleaf Pine and Slash
Pine, commonly sheltering beneath the exfoliating bark of pine snags and logs
as well as the sloughing bark flakes present on live trees. Horn and Hanula
(2002) found that Longleaf Pine had significantly more loose, flaking bark
scales than Loblolly Pine, and documented greater arthropod abundance and
biomass on Longleaf Pine; they concluded that bark structure is responsible
for the greater arthropod abundance on Longleaf Pine. Interstices associated
with the continuously sloughing bark of mature Longleaf Pine and Slash Pine
support potential prey (roaches, spiders, silverfish; Horn and Hanula 2002)
and provide shelters for C. hentzi. Specimens of C. hentzi exposed by removing
bark flakes on live trees crawl rapidly over the outer layers of pine bark
before squeezing into small cracks or fissures on the trunk proper or beneath
flaking bark scales.
Naturally functioning examples of the major ecosystems inhabited by C. hentzi
(sandhill and pine flatwoods) are pyric, fire-controlled communities with biotas
that have evolved in response to frequent, low-intensity surface fires (Myers
1990). Pine snags and logs are continually created in these habitats via lightning
strikes, hot wildfires or prescribed fires, beetle infestations, and windfalls caused
by tornados and hurricanes (Earley 2004, Myers 1990). In addition to active diurnal
searches, future efforts (sorely needed to elucidate the life history of this
interesting scorpion) should consider drift-fence sampling and “blacklighting”
field methods. We encourage studies of Centruroides hentzi that investigate reproductive
biology, seasonal ecology (e.g., microhabitats preferred for refuges,
foraging, and feeding) and population demographics.
2012 D.J. Stevenson, G. Greer, and M.J. Elliott 595
D. Almquist, L. Carlile, J. Hill, and an anonymous reviewer contributed helpful suggestions
on the manuscript. J. Bauder, K. Briggs, A. Day, M. Deyrup, W. Dopson, L.
Durden, J. Jensen, D. Jones, J. Macey, R. Moulis, S. Osborn, P. Range, C. Ruckdeschel,
R. Shelley, D. Sissom, L. Smith, F. Snow, D. Steen, and B. Willis-Stevenson assisted with
various aspects of this study.
Diemer, J.E., and D.W. Speake. 1983. The distribution of the Eastern Indigo Snake, Drymarchon
corais couperi, in Georgia. Journal of Herpetology 17:256–264.
Earley, L.S. 2004. Looking for Longleaf: The Fall and Rise of an American Forest. The
University of North Carolina Press, Chapel Hill, NC. 322 pp.
Folkerts, G.W., M.A. Deyrup, and D.C. Sisson. 1993. Arthropods associated with xeric
Longleaf Pine habitats in the southeastern United States: A brief overview. Pp.
159–192, In S.M. Hermann (Ed.). Proceedings of the 18th Tall Timbers Fire Ecology
Conference, The Longleaf Pine Ecosystem: Ecology, Restoration, and Management.
Tall Timbers Research, Inc., Tallahassee, FL. 418 pp.
Gibbons, W., R.R. Haynes, and J.L. Thomas. 1990. Poisonous Plants and Venomous
Animals of Alabama and Adjoining States. University of Alabama Press, Tuscaloosa,
AL. 345 pp.
Granatosky, M.C., L.M. Wagner, and K.L. Krysko. 2011. Natural History Note—Osteopilus
septentrionalis (Cuban Treefrog): Prey. Herpetological Review 42:90.
Hanula, J.L., and R.T. Engstrom. 2000. Comparison of Red-cockaded Woodpecker
(Picoides borealis) nestling diet in old-growth and old-field Longleaf Pine (Pinus
palustris) habitats. American Midland Naturalist 144:370–376.
Horn, S., and J.L. Hanula. 2002. Comparison of arthropod prey of Red-cockaded
Woodpeckers on the boles of Longleaf and Loblolly Pines. Wildlife Society Bulletin
McNab, W.H. 1980. Climatic factors related to the range of Saw-Palmetto (Serenoa repens
(Bartr.) Small. American Midland Naturalist 103:204–208.
McReynolds, C.N. 2008. Microhabitat preferences for the errant scorpion, Centruroides
vittatus (Scorpiones, Buthidae). Journal of Arachnology 36:557–564.
Myers, R.L. 1990. Scrub and high pine. Pp. 150–193, In R.L. Myers and J.J. Ewel (Eds.).
Ecosystems of Florida. University of Central Florida Press, Orl ando, FL. 765 pp.
Muma, M.H. 1967. Scorpions, whip scorpions, and wind scorpions of Florida. Arthropods
of Florida and Neighboring Land Areas 4:1–28.
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org/explorer. Accessed November 2011.
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Biology of Scorpions. Stanford University Press, Stanford, CA. 587 pp.
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reevaluation. Brimleyana 21:57–68.
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(Say) and Centruroides hentzi (Banks) in the United States and Mexico (Scorpiones,
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2012 D.J. Stevenson, G. Greer, and M.J. Elliott 597
Appendix 1. New Centruroides hentzi localities for Georgia.
GEORGIA: Appling County: 15.9 km NE Baxley, Ten Mile Rd. at East River Rd. (17 R
384047, 3527372), 8 March, 2011, D. Stevenson (GMNH); 15.6 km NNE Baxley, Moody
Forest Natural Area (17 R 0376287, 3531785), 8 March 2011, D. Stevenson (GMNH).
Atkinson County: 12.2 km SSE Willacoochee (17 R 308351, 3457387), 29 January 2011,
D. Stevenson, G. Greer, J. Jensen (GMNH); 3.5 km E Willacoochee (17 R 308749,
3467960), 4 March 2011, D. Stevenson (GMNH). Bacon County: 8.6 km ENE Alma,
Mallard Rd. at St. Hwy. 203 (17 R 369779, 3491367), 15 March 2011, D. Stevenson
(GMNH). Baker County: 1.9 km S St. Hwy. 91 along Ichawaynochaway Creek, Joseph
W. Jones Ecological Research Center (16 R 739873, 3454295), 7 April 2011, G. Greer
(GMNH). Ben Hill County: 10.9 km E Rebecca, St. Hwy. 90, 4.8 km E. of St. Hwy. 233
(17 R 274966, 3524501), 27 April 2011, G. Greer (GMNH). Berrien County: 6.8 km ESE
Alapha, Cty. Rd. 237 at St. Hwy. 32 (17 R 295395, 3473395), 15 March 2011, D. Stevenson
(GMNH). Brantley County: 7.8 km SE Hortense, St. Hwy. 110 at Fin Dig Rd. (17
R 416399, 3464621), 14 April 2011, D. Stevenson (GMNH); 6.2 km WSW Waynesville,
St. Hwy. 259 at St. Hwy. 82 (17 R 418755, 3454159), 20 October 2011, D. Stevenson
(GMNH). Bryan County: 12.4 km SSE Pembroke, Fort Stewart (17 S 442643, 3543334),
29 December 2011, D. Stevenson (GMNH). Bulloch County: Statesboro, 2007 (GSU);
Statesboro, 2008 (GSU); Statesboro, 16 April 2009, M. Sutherland (GSU); Statesboro,
Georgia Southern University Campus, April, 2009, L. Durden (GSU). Camden County:
3.1 km NW Jerusalem on Old Post Rd. (17 R 416547, 3429096), 20 October 2011, D.
Stevenson (GMNH); 3.7 km SW Jerusalem on St. Hwy. 252 (17 R 415853, 3425985), 20
October 2011, D. Stevenson (GMNH); Little Cumberland Island (17 R 460798, 3424541),
20 November 2011, C.W. Dopson, Jr. (GMNH). Candler County: 8.0 km NW Cobbtown
(17 S 386299, 3577097), 8 March 2011, D. Jones (GMNH); 8.0 km NW Cobbtown (17
S 386299, 3577097), 21 November 2011, D. Stevenson (GMNH). Charlton County:
12.2 km N Folkston at Newell (17 R 402488, 3423527), 31 March, 2011, D. Stevenson
(GMNH). Coffee County: 10.3 km SE Douglas on St. Hwy 158 (17 R 333390, 3482279),
11 July 2011, D. Stevenson (GMNH). Colquitt County: 3.2 km S Doerun on St. Hwy.
133, Doerun Wildlife Management Area (17 R 225483, 3465041), 7 April 2011, G. Greer
(GMNH). Decatur County: 7 km SSW Reynoldsville, Silver Lake Wildlife Management
Area (16 R 722619, 3410966), 29 May 2011, G. Greer and C. Reuter (GMNH). Echols
County. 16.2 km ESE Statenville, St. Hwy. 94 at Toms Creek (17 R 321696, 3395337),
23 December 2011, D. Stevenson and K. Briggs (GMNH); 5.9 km NW Statenville, St.
Hwy. 94 at Rader Rd. (17 R 300525, 3401217), 23 December 2011, D. Stevenson and K.
Briggs (GMNH). Evans County: 4.7 km SE Daisy, Evans Co. Public Fishing Area (17 S
425449, 3555272), 21 March 2011, D. Stevenson (GMNH). Glynn County: 4.1 km SSE
Waynesville, Post Rd. at County Line Rd. (17 R 426819, 3451749), 14 April 2011, D.
Stevenson (GMNH); Jekyll Island, Riverview Drive (17 R 459948, 3435229), 20 October
2011, D. Stevenson (GMNH); St. Simons Island, Lawrence Drive (17 R 466913,
3460017), 2 November 2011, G. Greer (GMNH). Irwin County: 10.6 km SW Ocilla (17
R 275593, 3490035), 25 February 2011, D. Stevenson and K. Briggs (GMNH); 10.6
km SW Ocilla (17 R 275593, 3490035), 24 March 2011, J. Jensen (GMNH). Jeff Davis
County: 7.5 km W Snipesville, Flat Tub Wildlife Management Area (17 R 326713,
3515519), 27 March 2011, D. Stevenson (GMNH). Liberty County: 5.8 km NNE Hinesville,
Fort Stewart (17 R 445190, 3529393), 3 May 2011, D. Stevenson and J. Macey
(GMNH). Long County: 13.0 km WSW Ludowici, Griffin Ridge Wildlife Management
Area (17 R 423947, 3507488), 3 March 2011, D. Stevenson and A. Day (GMNH);13. 0
km WNW Townsend, Townsend Wildlife Management Area (17 R 437179, 3492994),
598 Southeastern Naturalist Vol. 11, No. 4
7 March 2011, D. Stevenson (GMNH); 6.8 km SE Glennville (17 R 418489, 3531142),
23 April 2011, D. Stevenson (GMNH); 13.0 km WSW Ludowici, Griffin Ridge Wildlife
Management Area (17 R 423947, 3507488), 8 November 2011, D. Stevenson (GMNH).
McIntosh County: 7.4 km SW Townsend, Old River Rd. at Hardshell Rd. (17 R 445313,
3483977), 16 March 2011, D. Stevenson and D. Jones (GMNH); 6.8 km SSW Eulonia
at St. Hwy. 17 (17 R 458107, 3482138), 20 October 2011, D. Stevenson (GMNH).
Miller County: 9.5 km NW Colquitt, Mayhaw Wildlife Management Area (16 R 656540,
3472839), 18 August 2009, A. Cressler (Photograph) (GMNH). Montgomery County: 5.6
km NNE Ailey (17 S 353984, 3567570), 27 April 2011, D. Stevenson (GMNH); 2.5 km
W Uvalde, Cty. Rd. 125, 0.2 km E of Bud Denton Rd. (17 S 355448, 3544066), 27 April
2011, G. Greer (GMNH). Pierce County: 6.0 km N Blackshear, Oak Hill Rd. at St. Hwy.
121/15 (17 R 382023, 3470220), 14 April 2011, D. Stevenson (GMNH). Tattnall County:
14 km SW Glennville, Big Hammock Natural Area at Mac Phillips Rd. (17 R 400787,
3525929), 8 March 2011, D. Stevenson (GMNH); 14.3 km W Glennville on Old River
Rd. (17 R 388979, 3534136), 1 November 2011, D. Stevenson (GMNH). Telfair County,
7.2 km SE McRae, St. Hwy. 149, 2.6 km SW of St. Hwy. 441 (17 S 324694, 3544085), 23
March 2011, D. Stevenson (GMNH); 10.9 km ENE Jacksonville, Horse Creek Wildlife
Management Area (17 R 323469, 3523262), 16 April 2011, D. Stevenson and J. Bauder
(GMNH). Toombs County: 5.0 km N Lyons, St. Hwy. 130 at Piney Green Church Rd.
(17 S 373836, 3568667), 23 March 2011, D. Stevenson and G. Greer (GMNH); 4.8 km
SW Normantown, Claxton Rd. at St. Hwy. 297 (17 S 367390, 3572168), 26 October, D.
Stevenson (GMNH); Lyons, 1 March 2010, B. Robinson (GSU). Treutlen County: 5.6 km
NE Soperton, Cty. Rd. 183 (17 S 353622, 3587694), 21 October 2011, G. Greer (GMNH).
Ware County: 22.2 km NW Waycross, N side of St. Hwy 82 (17 R 349642, 3460238), 15
March 2011, D. Stevenson (GMNH). Wayne County, 9.2 km SW Jesup, St. Hwy 203 at
St. Hwy. 84 (17 R 408309, 3492158), 15 March 2011, D. Stevenson (GMNH); 9.4 km
E Gardi, Penholloway Wildlife Management Area (17 R 433550, 3489128), 14 August
2011, D. Stevenson (GMNH); 13.8 km SSE Gardi, Wire Rd. at Flowers Break Rd. (17
R 428498, 3476334), 13 October 2011, D. Stevenson (GMNH). Wheeler County: 2.1
km NE Lumber City (17 R 342944, 3535166), 26 February 2011, D. Stevenson and K.
Briggs (GMNH). Wilcox County: 18.2 km SSE Abbeville, St. Hwy. 129 at Bowens Mill
Fish Hatchery (17 R 291398, 3526066), 25 April 2011, D. Stevenson (GMNH). Worth
County: 9.6 km S Sylvester, St. Hwy. 33, 5.3 km S of Dixon Rd. (17 R 229100, 3476529),
7 April 2011, G. Greer (GMNH).