Euphyes dion - (Edwards, 1879)
Dion Skipper
Other English Common Names: Dion skipper
Synonym(s): Euphyes alabamae ;Euphyes macguirei
Taxonomic Status: Accepted
Related ITIS Name(s): Euphyes dion (W. H. Edwards, 1879) (TSN 706610)
French Common Names: hespérie farouche
Unique Identifier: ELEMENT_GLOBAL.2.115869
Element Code: IILEP77030
Informal Taxonomy: Animals, Invertebrates - Insects - Butterflies and Moths - Butterflies and Skippers
 
Kingdom Phylum Class Order Family Genus
Animalia Mandibulata Insecta Lepidoptera Hesperiidae Euphyes
Genus Size: C - Small genus (6-20 species)
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Concept Reference
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Concept Reference: Opler, P. A., and A. D. Warren. 2002. Butterflies of North America. 2. Scientific Names List for Butterfly Species of North America, north of Mexico. C.P. Gillette Museum of Arthropod Diversity, Department of Bioagricultural Sciences and Pest Management, Colorado State University, Fort Collins, Colorado. 79 pp.
Concept Reference Code: B02OPL01EHUS
Name Used in Concept Reference: Euphyes dion
Conservation Status
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NatureServe Status

Global Status: G4
Global Status Last Reviewed: 13Sep2015
Global Status Last Changed: 01Sep1998
Ranking Methodology Used: Ranked by inspection
Rounded Global Status: G4 - Apparently Secure
Nation: United States
National Status: N4 (01Sep1998)
Nation: Canada
National Status: N4 (13Sep2015)

U.S. & Canada State/Province Status
United States Alabama (SU), Arkansas (SU), Connecticut (S2), Delaware (S1), Florida (S2S3), Georgia (S2S4), Illinois (S3), Indiana (S2S3), Iowa (S3), Kansas (S2S3), Kentucky (S3), Louisiana (SU), Maryland (S3), Massachusetts (S1S2), Michigan (S3S4), Minnesota (S4), Mississippi (S2S4), Missouri (S2S4), Nebraska (S2), New Jersey (S4), New York (S3), North Carolina (S4), North Dakota (S1), Ohio (S4), Oklahoma (S3), Pennsylvania (S2), South Carolina (SNR), Tennessee (S3?), Texas (SNR), Vermont (S2), Virginia (S4), Wisconsin (S4)
Canada Ontario (S4), Quebec (S3)

Other Statuses

NatureServe Global Conservation Status Factors

Other NatureServe Conservation Status Information

Distribution
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U.S. States and Canadian Provinces
Color legend for Distribution Map
Endemism: occurs (regularly, as a native taxon) in multiple nations

U.S. & Canada State/Province Distribution
United States AL, AR, CT, DE, FL, GA, IA, IL, IN, KS, KY, LA, MA, MD, MI, MN, MO, MS, NC, ND, NE, NJ, NY, OH, OK, PA, SC, TN, TX, VA, VT, WI
Canada ON, QC

Range Map
No map available.


U.S. Distribution by County Help
State County Name (FIPS Code)
CT Fairfield (09001), Litchfield (09005)
DE Sussex (10005)
FL Clay (12019), Escambia (12033), Franklin (12037), Levy (12075), Liberty (12077), Okaloosa (12091), Santa Rosa (12113), Wakulla (12129), Walton (12131), Washington (12133)
IA Black Hawk (19013), Bremer (19017), Buchanan (19019), Butler (19023), Calhoun (19025), Cerro Gordo (19033), Chickasaw (19037), Dickinson (19059), Fayette (19065), Hancock (19081), Kossuth (19109), Lucas (19117), Osceola (19143), Pocahontas (19151)
IN La Porte (18091), Lake (18089), Porter (18127), Starke (18149)
MA Berkshire (25003), Hampshire (25015)
ND Ransom (38073)
PA Adams (42001), Bradford (42015), Tioga (42117), Warren (42123)
VT Addison (50001), Bennington (50003), Chittenden (50007), Grand Isle (50013), Lamoille (50015), Rutland (50021), Windham (50025)
* Extirpated/possibly extirpated
U.S. Distribution by Watershed Help
Watershed Region Help Watershed Name (Watershed Code)
01 West (01080107)+, Middle Connecticut (01080201)+, Housatonic (01100005)+, Saugatuck (01100006)+
02 Hudson-Hoosic (02020003)+, Broadkill-Smyrna (02040207)+, Tioga (02050104)+, Upper Susquehanna-Tunkhannock (02050106)+, Monocacy (02070009)+, Pokomoke-Western Lower Delmarva (02080111)+
03 Lower St. Johns (03080103)+, Waccasassa (03110101)+, Apalachee Bay-St. Marks (03120001)+, Lower Ochlockonee (03120003)+, Apalachicola (03130011)+, New (03130013)+, Choctawhatchee Bay (03140102)+, Yellow (03140103)+, Blackwater (03140104)+, Pensacola Bay (03140105)+, Perdido (03140106)+, Lower Choctawhatchee (03140203)+
04 Little Calumet-Galien (04040001)+, Otter Creek (04150402)+, Missiquoi River (04150407)+, Lake Champlain (04150408)+
05 Upper Allegheny (05010001)+, Conewango (05010002)+
07 Upper Wapsipinicon (07080102)+, Upper Cedar (07080201)+, Winnebago (07080203)+, West Fork Cedar (07080204)+, Middle Cedar (07080205)+, Upper Iowa (07080207)+, East Fork Des Moines (07100003)+, Middle Des Moines (07100004)+, North Raccoon (07100006)+, Lake Red Rock (07100008)+, Kankakee (07120001)+, Chicago (07120003)+
09 Lower Sheyenne (09020204)+
10 Little Sioux (10230003)+
+ Natural heritage record(s) exist for this watershed
* Extirpated/possibly extirpated
Ecology & Life History
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Non-Migrant: N
Locally Migrant: N
Long Distance Migrant: N
Palustrine Habitat(s): Bog/fen, HERBACEOUS WETLAND, Riparian, SCRUB-SHRUB WETLAND
Habitat Comments: Generally open to shrubby sedge wetlands and occasionally in northern New Jersey (definitely subspecies DION) even in openings in limey red maple swamps. Subspecies DION northward generally on calcareous soils associated with large sedges like CAREX LACUSTRIS. Coastal plain and southeastern populations (mostly subspecies ALABAMAE) in a great variety of sedge situations from swales in wet pine barrens (especially in southern New Jersey), to bogs, roadside ditches and a very good colonizer. Southeastern and coastal plain populations often associated with CAREX HYALINOLEPIS or C. STRIATA. Both subspecies sometimes with SCIRPUS CYPERINUS in ditches (Schweitzer).
Economic Attributes Not yet assessed
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Management Summary Not yet assessed
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Population/Occurrence Delineation
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Group Name: Euphyes, Poanes and other Wetland Skippers

Use Class: Not applicable
Minimum Criteria for an Occurrence: A location where the species occurs, or has occurred, where there is potential for persistence or regular recurrence. Minimally a wetland with the larval foodplant where at least one adult has been verified by a photograph or preferably a specimen. Photographs must be diagnostic and will probably need to show both wing surfaces, and there may be circumstances where only a specimen will suffice. Specimens are much easier to obtain.
Mapping Guidance: Habitat patches are usually discrete, small and easily defined by the dominance of the foodplant. Most or all other species use both open and semi-shaded patches but E. DUKESII is a forest or woodland species. Consult the habitat and food comments fields for species-specific information on what constitutes suitable habitat when mapping occurrences of these species.
Separation Distance for Unsuitable Habitat: 2 km
Separation Distance for Suitable Habitat: 5 km
Alternate Separation Procedure: Within a wetland complex consider multiple colonies as one metapopulation by using the suitable habitat distance.
Separation Justification: Adults of these species sometimes to often (e.g. E. dion alabamae) stray out of habitat and even the sedentary P. massasoit as well as both subspecies of E. dion will move a kilometer or more for nectar. However, habitats are often small (a few hectares) and populations often appear small (20 or less on a given day) so relatively conservative separation distances seem reasonable. Certainly a distance of a few km will provide a large amount of separation even if not a complete lack of gene flow. However apply the suitable habitat figure when two collection sites are along the same river, same wetland complex or in other circumstances where at least a few patches of foodplant occur in wet spots between them. Justification for this includes observations of not less than three tiny transient colonies of Euphyes dion alabamae in Cumberland County New Jersey in habitat patches of less than 0.1 hectare with no known source habitat within a kilometer. Thus females do find and oviposit in tiny patches and adults from these as well as the dispersing females themselves should connect multiple source colonies. Suitable habitat patches more than a kilometer in any dimension are rare, so generally colonies more than a few kilometers apart are separate occurrences unless obviously connected. However in such rare cases where habitats are really extensive with foodplant throughout or even dominant there is not reason to believe these skippers should not be likewise.
Inferred Minimum Extent of Habitat Use (when actual extent is unknown): 1 km
Inferred Minimum Extent Justification: The inferred extent is nearly always at least the entire contiguous habitat/foodplant patch since these are usually only a few dozens of hectares at most. Colonies can persist at least decades in under a hectare of really good habitat. If the habitat is really several kilometers in extent it will usually be fully occupied (apparently nearly always so for the better known species) but cap inferred extent at this distance pending further observation.
Date: 14Sep2001
Author: Schweitzer, Dale F.
Population/Occurrence Viability
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U.S. Invasive Species Impact Rank (I-Rank) Not yet assessed
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Authors/Contributors
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Element Ecology & Life History Edition Date: 08May2001

Zoological data developed by NatureServe and its network of natural heritage programs (see Local Programs) and other contributors and cooperators (see Sources).

References
Help
  • Handfield, Louis. 1999. Le guide des papillons du Québec. Vol. 1 Les Éditions Brochet. Boucherville. Québec. 982 pages + planches

  • Miller, J.Y. (ed.). 1992. The common names of North American butterflies. Smithsonian Institution Press, Washington. 177p.

  • Opler, P. A., and A. D. Warren. 2002. Butterflies of North America. 2. Scientific Names List for Butterfly Species of North America, north of Mexico. C.P. Gillette Museum of Arthropod Diversity, Department of Bioagricultural Sciences and Pest Management, Colorado State University, Fort Collins, Colorado. 79 pp.

  • Pelham, J. P. 2008. A catalogue of the butterflies of the United States and Canada with a complete bibliography of the descriptive and systematic literature. The Journal of Research on the Lepidoptera. Volume 40. 658 pp.

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