Rough green snake
Opheodrys aestivus
 
ITIS Species Code:   174172         NatureServ Element Code:   ARADB23010
 
Taxa: 
Order: 
Family: 
Reptilia
Squamata
Colubridae
NatureServe Global Rank: 
NatureServe State (NC) Rank: 
 
G5
S5
 
Federal Status: 
NC State Status: 
 
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HEXAGONAL KNOWN RANGE:PREDICTED DISTRIBUTION:
 
SUMMARY OF STATEWIDE PREDICTED DISTRIBUTION:
 
Land Unit

US Fish & Wildlife Service
US Forest Service
US National Park Service
US Department of Defense
NC State Parks
NC University System
NC Wildlife Res. Com.
NC Forest Service
NC Div. of Coastal Mgmt.
Local Governments
Non-Governmental Org.
Other Public Lands
Private Lands

GAP Status 1-2
All Protected Lands
Statewide
 
Hectares

55,310.94
63,092.79
56,900.70
10,508.58
4,023.81
18,639.90
45,221.94
6,314.82
2,600.73
970.11
8,812.08
636.39
2,168,719.65

132,288.54
271,149.36
2,441,752.44
 
Acres

136,676.28
155,905.65
140,604.66
25,967.26
9,943.05
46,060.19
111,745.83
15,873.65
6,426.54
2,397.19
21,775.12
1,572.55
5,359,021.92

327,161.43
670,293.92
6,033,969.90
% of Dist. on
Prot. Lands

20.4 %
23.3 %
20.5 %
3.9 %
1.5 %
6.9 %
16.5 %
2.3 %
1.0 %
3.2 %
3.2 %
0.2 %
< 0.1 %

48.8 %
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% of Dist. on
All Lands

2.3 %
2.6 %
2.3 %
0.4 %
0.2 %
0.8 %
1.9 %
0.3 %
0.1 %
< 0.1 %
0.4 %
< 0.1 %
88.8 %

5.4 %
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HABITAT DESCRIPTION:
NATURE SERVE GLOBAL HABITAT COMMENTS:

Typically in dense vegetation (vines, shrubs, trees) near water; often at forest edges or in fairly open forests; also overgrown pasture, tallgrass prairie, thickets. Mostly arboreal but less so in spring and fall. In Arkansas, avoided basking (Plummer 1993). Occupies vegetation above ground at night in warmer months; underground in cold weather.

Eggs are laid under objects in damp areas (Ashton and Ashton 1981), in rotting logs (Goldsmith 1984), or in tree hollows. May nest communally. In Arkansas, gravid females moved 5-75 m (average 36 m) terrestrially away from lake shore and oviposited in small chambers within the hollowed interiors of small living trees, 25-300 cm above ground; individuals may return to specific tree each year (Plummer 1989, 1990).

 
MODELING DESCRIPTION:
Occupied Landcover Map Units:
Code NameDescription NC Natural Heritage Program Equivalent
124 Maritime Scrubs and Tidal Shrublands Coastal shrubs including wax-myrtle, swamp rose, alder, yaupon, and greenbriar. Maritime Shrubs, Salt Shrub
372 Interdune Herbaceous Wetlands Dune swales with permanently flooded to intermittently exposed hydrology. Species composition depends on salinity and can include cut grass, spike-rush, mosquito fern, and hornwort. Interdune Pond, Maritime Wet Grasslands
371 Maritime Grasslands Dune grass community consisting of sea oats and beach grasses. Dune grass, Maritime dry grassland
75 Tidal Swamp Forest Swamp tupelo dominated forest with or without black tupelo and/or cypress trees. Restricted to the tidal zones in the coastal plain. May have inclusions of coastal red cedar woodlands. Tidal cypress - gum swamp
121 Maritime Pinelands Loblolly forests and woodlands of the outer coastal plain. Estuarine Fringe Loblolly Pine Forest
17 Maritime Forests and Hammocks Maritime forests and woodlands dominated by live or sand laurel oak. Estuarine Fringe forests dominated by loblolly pine. Coastal Fringe Evergreen Forest, Maritime Deciduous Forest, Maritime Deciduous Forest
126 Interdune Wooded Depression Swamp Includes swamps dominated by sweetbay and swampbay or dogwood dominated forests. Maritime Shrub Swamp, Maritime Swamp Forest
173 Coastal Plain Riverbank Shrubs Shrub dominated riverbanks, commonly dominated by willows and/or alders. Sand and Mud Bar
50 Coastal Plain Mixed Bottomland Forests Includes forests dominated by a variety of hardwood species, including sweetgum, cottonwood, red maple. Coastal Plain Bottomland Hardwood (in part), Coastal Plain Levee Forest
49 Coastal Plain Oak Bottomland Forest Bottomland forests dominated by deciduous oak alliances. Oaks represented can include swamp chestnut, cherrybark, willow, and/or overcup oak. Inclusions of loblolly pine temporarily flooded forests occur in patches. Hydrology is temporarily to seasonally flooded. Coastal Plain Bottomland Hardwoods (in part) blackwater subtype, brownwater subtype
158 Coastal Plain Nonriverine Wet Flat Forests Loblolly pine - Atlantic white-cedar - red maple - swamp tupelo saturated forests as well as forests dominated by loblolly, sweetgum, and red maple in non-riverine flats. Non-riverine Wet Hardwood Forest
41 Peatland Atlantic White-Cedar Forest Dense stands of Atlantic white cedar with saturated hydrology. Can include swamp tupelo, red maple, and pond pines with a moderate shrub and herb layer. Peatland Atlantic White-Cedar Forest
15 Seepage and Streamhead Swamps Includes extensive peat flats in the coastal plain, dominated by swamp tupelo, maples, and Atlantic white cedar alliances. In the sandhills includes streamhead pond pine and bay forests alliances. Saturated hydrology. Bay Forest, Small Depression Pocosin, Streamhead Atlantic White Cedar Forest, Streamhead Pocosins
30 Cypress-Gum Floodplain Forests Swamps dominated by black or swamp tupelo with or without Taxodium. Seasonally to semi-permanently flooded hydrology. Cypress-Gum Swamps
78 Pond-Cypress - Gum Swamps, Savannas and Lakeshores Cypress dominated swamps and lakeshores. Can include bays dominated by pond cypress or shorelines of coastal plain lakes with a narrow band of cypress. Non-riverine Swamp Forest, Natural Lakeshores (in part)
385 Oak Bottomland Forest and Swamp Forest The swamp chestnut oak, cherrybark oak, shumard oak and sweetgum alliance is one representative. Other alliances are dominated by water, willow, and overcup oaks. Swamp forests can be dominated by sweetgum, red maple, and black gum being dominant. Loblolly can occur in combination with sweetgum and red maple, or with tulip poplar. Includes saturated and semi- to permanently flooded forests in the mountains. Piedmont/Mountain Bottomland Forest, Piedmont/Mountain Swamp Forest
63 Coastal Plain Mesic Hardwood Forests Beech dominated forests with white oak and northern red oak as possible co-dominants. Dry-mesic to mesic forests on slopes and small stream bottoms in the coastal plain. Mesic Mixed Hardwood Forest, Basic Mesic Forests
138 Coastal Plain Dry to Dry-Mesic Oak Forests Oak dominated forests of the coastal plain. Includes white oak forests with water oak or northern red oak and hickories as co-dominants. Dry Mesic Oak Hickory Forest, Basic Oak Hickory Forest, Dry Oak Hickory Forest
87 Pocosin Woodlands and Shrublands Includes pond pine woodland, low pocosin and high pocosin shrub dominated areas. Canebrakes and bay forests may be present. Pond Pine Woodlands, Peatland Canebrake, Small Depression Pocosin
67 Wet Longleaf or Slash Pine Savanna Wet flatwoods and pine savannas, typically dominated by longleaf pines, but slash or pond pines may be the dominant pines. Wet Pine Flatwoods
97 Mesic Longleaf Pine Longleaf pine woodlands without a major scrub oak component. Slash or loblolly pines may be present as well. Mesic Pine Flatwoods
267 Riverbank Shrublands Riverside shrubs with temporarily flooded hydrologies. Found in the both the Mountains and Piedmont. Containing dominants such as smooth alder and a Carolina or black willows. Sand and Mud Bar
269 Floodplain Wet Shrublands Saturated shrublands of the Piedmont, includes buttonbush, swamp-loosestrife, decodon and alders. Piedmont/mountain Semipermanent Impoundment
384 Piedmont/Mountain Mixed Bottomland Hardwood Forests Includes temporarily to seasonally forests dominated by hardwood species. Hardwoods include sweetgum, red maple, sycamore which co-occur in a mosaic of bottomland and levee positions. Includes alluvial hardwood forests in the mountains. Hemlock and white pine may occur as inclusions, but are generally mapped separately. Piedmont/Mountain Alluvial Forest, Piedmont/Mountain Levee Forest
180 Agricultural Crop Fields Farm fields used for row crops. No equivalent
205 Agricultural Pasture/Hay and Natural Herbaceous Farm fields used for pasture grass or hay production, as well as old fields dominated by native and exotic grasses. No equivalent
213 Barren; quarries, strip mines, and gravel pits Quarries, strip mines, or gravel pits. No equivalent
214 Barren; bare rock and sand Areas of bare rock, sand or clay. No equivalent
60 Sand Exposed sand, predominantly in the sandhills region where disturbance or the extreme site conditions prevent natural regeneration. No equivalent
202 Residential Urban Includes vegetation interspersed in residential areas. Includes lawns, mixed species woodlots, and horticultural shrubs. Vegetation accounts for between 20 - 70% of the cover. No equivalent
517 Hemlock Floodplain Forest Alluvial forest with hemlock and/or white pine in mountains and western piedmont. Hydrology is generally temporarily to seasonally flooded. Canada Hemlock Forest
521 Spruce/Fir Forest High Elevation Frazer-Fir - Red Spruce, Red Spruce and Red-Spruce-Yellow Birch Forests. Tree densities included here include both woodland to forest density. Highly intermixed with Northern Hardwoods, Grassy Balds, and Shrub Balds. Red Spruce--Fraser Fir Forest, Fraser Fir Forest
522 Northern Hardwoods High Elevation forests including yellow birch, American beech, and yellow buckeye. Includes forests with Hemlock and Yellow Birch. Northern Hardwoods Forest, Boulderfield Forest
523 Grassy Bald High Elevation grassy balds including Pennsylvania sedge, mountain oatgrass, as well as shrubby areas dominated by Alleghany and smooth blackberry. Grassy Bald
524 Shrub Bald Variable phenologies, predominantly evergreen balds with rhododendon and Mountain laurels. Deciduous shrubs including green alder and Alleghany and smooth blackberry are included as well. Red Oak - Chestnut Oak Woodlands may be included in cases where the density of the woodland species is low and the shrub component is dense. Heath Bald
525 Appalachian Oak Forest A variety of oak forest types including Black, White, Scarlet Oaks in dry to mesic situations. Includes forests historically co-dominated by American Chestnut. High Elevation Red Oak Forest, Montane White Oak Forest
526 Appalachian Cove Forest Mixed Mesophytic forests of the mountains. Includes tuliptree, basswood, yellow buckeye and surgar maple. This class is mapped to include cove forests dominated or co-dominated by hemlock. Rich Cove Forest, Acidic Cove Forest
527 Appalachian Hemlock Upland hemlock forests of the moutains region. Vary from side slopes to steep slope positions. Canada Hemlock Forest
533 Appalachian Swamp Forest Evergreen and deciduous forests with saturated hydrologies. This class may contain a variety of trees species, including hemlock - red maple, pitch pine, and white pine forests. Swamp Forest-Bog Complex, Southern Appalachian Bog, Southern Appalachian Fen
534 Appalachian Wet Shrubland/ Herbaceous Saturated shrubs and herbaceous vegetation. Often mapped as an inclusion in Appalachian Swamp Forest. Southern Appalachian Bog, Southern Appalachian Fen
535 Talus/Outcrops/Cliffs Includes seep talus slopes with sparce vegetation, as well as outcrops including, granitic outcrops. Some outcrops will have been mapped as barren rock. No equivalent
View Entire Landcover Legend
 
Additional Spatial Constraints:
Exclude all area outside of known range.
Limited to edge habitats including forest/field borders, shrublands and woodlands.
 
CITATIONS:
Plummer, M. V. 1990. Nesting movements, nesting behavior, and nest sites of green snakes (OPHEODRYS AESTIVUS) revealed by radiotelemetry. Herpetologica 46:190-195.

Plummer, M. V. 1993. Thermal ecology of arboreal green snakes (OPHEODRYS AESTIVUS). J. Herpetol. 27:254-260.

Plummer, M. V. 1997. Population ecology of green snakes (OPHEODRYS AESTIVUS) revisited. Herpetological Monographs 11:102-123.

Conant, R. and J. T. Collins. 1991. A field guide to reptiles and amphibians:eastern and central North America. Third edition. Houghton Mifflin Co., Boston, Massachusetts. 450 pp.

Grobman, A. 1992. On races, clines, and common names in OPHEODRYS. Herpetol. Rev. 23:14-15.

Plummer, M. V. 1989. Observations on the nesting ecology of green snakes (OPHEODRYS AESTIVUS). Herpetol. Rev. 20:87-89.

Fitch, H. S. 1970. Reproductive cycles of lizards and snakes. Univ. Kansas Museum Natural History Miscellaneous Publication 52:1-247.

Minton, S. A., Jr. 1972. Amphibians and reptiles of Indiana. Indiana Academy Science Monographs 3. v + 346 pp.

Goldsmith, S. K. 1984. Aspects of the natural history of the rough green snake, OPHEODRYS AESTIVUS (Colubridae). Southwest. Nat. 29:445-452.

Mount, R. H. 1975. The Reptiles and Amphibians of Alabama. Auburn University Agricultural Experiment Station, Auburn, Alabama. vii + 347 pp.

Behler, J. L., and F. W. King. 1979. The Audubon Society field guide to North American reptiles and amphibians. Alfred A. Knopf, New York. 719 pp.

Ashton, R. E., Jr., and P. S. Ashton. 1981. Handbook of Reptiles and Amphibians of Florida. Part One:The Snakes. Windward Pub. Co., Miami, Florida. 176 pp.

Plummer, M. V. 1985. Demography of green snakes (OPHEODRYSAESTIVUS). Herpetologica 41:373-381.

Plummer, M. V. 1985. Growth and maturity in green snakes (OPHEODRYS AESTIVUS). Herpetologica 41:28-33.

Collins, J. T. 1982. Amphibians and reptiles in Kansas. Second edition. Univ. Kansas Mus. Nat. Hist., Pub. Ed. Ser. 8. xiii + 356 pp.

Grobman, A. B. 1984. Scutellation variation in OPHEODRYS AESTIVUS. Bull. Florida State Mus., Biol. Sci. 29(3):153-170.

Tennant, A. 1984. The Snakes of Texas. Texas Monthly Press, Austin, Texas. 561 pp.

Collins, J. T. 1990. Standard common and current scientific names for North American amphibians and reptiles. SSAR Herpetol. Circular No. 19. 41 pp.

Collins, J. T. 1992. Reply to Grobman on variation in OPHEODRYS AESTIVUS. Herpetol. Rev. 23:15-16.

Oldham, J. C., and H. M. Smith. 1991. The generic status of the smooth green snake, OPHEODRYS VERNALIS. Bull. Maryland Herp. Soc. 27(4):201-215.

10 March 2005
 
This data was compiled and/or developed by the North Carolina GAP Analysis Project.

For more information please contact them at:
NC-GAP Analysis Project
Dept. of Zoology, NCSU
Campus Box 7617
Raleigh, NC 27695-7617
(919) 513-2853
www.basic.ncsu.edu/ncgap