Gillette's Checkerspot - Euphydryas gillettii
[From Ferris and Brown 1981; Scott 1986; Glassberg 2001; Pyle 2002] Forewing 2.0-2.5 cm. Upperwings predominantly black on the basal 2/3, with red and white spot-bands, a distinctive orange-red submarginal band across the predominately dark-brown to black wings; underwings with alternating bands of cream and bright brick-red with black veins and borders of spot-bands.
One flight; mostly late June to July (late July to mid-August for subalpine sites), with a short flight season (Scott 1986; Glassberg 2001); mid-June to late July in British Columbia (Guppy and Shepard 2001); June to mid-August (Williams et al. 1984).
The orange-red submarginal band across the predominately dark-brown to black forewings and hindwings is distinctive.
In the Rocky Mountains, from southern Alberta and extreme eastern British Columbia south through northern Idaho, western Montana and western Wyoming (Ferris and Brown 1981; Scott 1986; Williams 1988; Glassberg 2001); between 975-2620m elevation. In Montana, reported from most counties in the western (mountainous) third of the state (Kohler 1980; Stanford and Opler 1993); between 975-2225 m elevation. Locally rare (Glassberg 2001).
Observations in Montana Natural Heritage Program Database
Number of Observations:
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Map Help and Descriptions
(Observations spanning multiple months or years are excluded from time charts)
Montane areas in wet meadows, marshy sites, along small streams, open riparian habitat; tree canopy predominantly lodgepole pine, Engelmann spruce, subalpine fir, sometimes with willow, cottonwood, aspen, often in fire-disturbed locations (Williams et al. 1984; Scott 1986; Williams 1988, 1995; Guppy and Shepard 2001). Habitat in Montana as described above (Williams 1988); in Glacier National Park, reported in montane mesic meadows and woodlands (Debinski 1993).
Ecological Systems Associated with this Species
- Details on Creation and Suggested Uses and Limitations
How Associations Were Made
We associated the use and habitat quality (common or occasional) of each of the 82 ecological systems mapped in Montana for
vertebrate animal species that regularly breed, overwinter, or migrate through the state by:
- Using personal observations and reviewing literature that summarize the breeding, overwintering, or migratory habitat requirements of each species (Dobkin 1992, Hart et al. 1998, Hutto and Young 1999, Maxell 2000, Foresman 2012, Adams 2003, and Werner et al. 2004);
- Evaluating structural characteristics and distribution of each ecological system relative to the species' range and habitat requirements;
- Examining the observation records for each species in the state-wide point observation database associated with each ecological system;
- Calculating the percentage of observations associated with each ecological system relative to the percent of Montana covered by each ecological system to get a measure of "observations versus availability of habitat".
Species that breed in Montana were only evaluated for breeding habitat use, species that only overwinter in Montana were only evaluated for overwintering habitat use, and species that only migrate through Montana were only evaluated for migratory habitat use.
In general, species were listed as associated with an ecological system if structural characteristics of used habitat documented in the literature were present in the ecological system or large numbers of point observations were associated with the ecological system.
However, species were not listed as associated with an ecological system if there was no support in the literature for use of structural characteristics in an ecological system, even if
point observations were associated with that system.
Common versus occasional association with an ecological system was assigned based on the degree to which the structural characteristics of an ecological system matched the preferred structural habitat characteristics for each species as represented in scientific literature.
The percentage of observations associated with each ecological system relative to the percent of Montana covered by each ecological system was also used to guide assignment of common versus occasional association.
If you have any questions or comments on species associations with ecological systems, please contact the Montana Natural Heritage Program's Senior Zoologist.
Suggested Uses and Limitations
Species associations with ecological systems should be used to generate potential lists of species that may occupy broader landscapes for the purposes of landscape-level planning.
These potential lists of species should not be used in place of documented occurrences of species (this information can be requested at: http://mtnhp.org/requests/default.asp
) or systematic surveys for species and evaluations of habitat at a local site level by trained biologists.
Users of this information should be aware that the land cover data used to generate species associations is based on imagery from the late 1990s and early 2000s and was only intended to be used at broader landscape scales.
Land cover mapping accuracy is particularly problematic when the systems occur as small patches or where the land cover types have been altered over the past decade.
Thus, particular caution should be used when using the associations in assessments of smaller areas (e.g., evaluations of public land survey sections).
Finally, although a species may be associated with a particular ecological system within its known geographic range, portions of that ecological system may occur outside of the species' known geographic range.
- Adams, R.A. 2003. Bats of the Rocky Mountain West; natural history, ecology, and conservation. Boulder, CO: University Press of Colorado. 289 p.
- Dobkin, D. S. 1992. Neotropical migrant land birds in the Northern Rockies and Great Plains. USDA Forest Service, Northern Region. Publication No. R1-93-34. Missoula, MT.
- Foresman, K.R. 2012. Mammals of Montana. Second edition. Mountain Press Publishing, Missoula, Montana. 429 pp.
- Hart, M.M., W.A. Williams, P.C. Thornton, K.P. McLaughlin, C.M. Tobalske, B.A. Maxell, D.P. Hendricks, C.R. Peterson, and R.L. Redmond. 1998. Montana atlas of terrestrial vertebrates. Montana Cooperative Wildlife Research Unit, University of Montana, Missoula, MT. 1302 p.
- Hutto, R.L. and J.S. Young. 1999. Habitat relationships of landbirds in the Northern Region, USDA Forest Service, Rocky Mountain Research Station RMRS-GTR-32. 72 p.
- Maxell, B.A. 2000. Management of Montana's amphibians: a review of factors that may present a risk to population viability and accounts on the identification, distribution, taxonomy, habitat use, natural history, and the status and conservation of individual species. Report to U.S. Forest Service Region 1. Missoula, MT: Wildlife Biology Program, University of Montana. 161 p.
- Werner, J.K., B.A. Maxell, P. Hendricks, and D. Flath. 2004. Amphibians and reptiles of Montana. Missoula, MT: Mountain Press Publishing Company. 262 p.
- Commonly Associated with these Ecological Systems
Forest and Woodland Systems
Recently Disturbed or Modified
Wetland and Riparian Systems
- Occasionally Associated with these Ecological Systems
Forest and Woodland Systems
Shrubland, Steppe and Savanna Systems
Larval food plants predominantly Lonicera involucrata and to a lesser extent Valeriana occidentalis (Williams et al. 1984; Williams and Bowers 1987). Oviposition reported on other plant species, including Castilleja, Pedicularis, Symphoricarpus, and Veronica; larvae feed on Plantago in captivity (Scott 1986; Williams 1988). Adults feed on flower nectar (including Achillia, Agoseris, Antennaria, Arnica, Aster, Chrysanthemum, Cirsium, Geranium, Geum, Helianthella, Heracleum, Polygonum, Potentilla, Rosa, Saxifraga, Senecio, Solidago, Valeriana) and mud (Williams 1988, 1995; Scott 2014).
Females lay eggs in masses on the undersides of host plant green leaves that tend to intercept morning sun; Wyoming masses in the Beartooth Mountains average 146 eggs (23-310 eggs), masses in the Teton Mountains average 130 eggs. Egg loss from masses ranges from 13-30%. Eggs hatch from July to September, 23-45 days after laying. Newly emerged larvae shortly migrate to the upper surface of leaves where they form a communal feeding web and remain together overwinter. Diapause (overwintering) can occur in L2-L4 instars, depending on duration prior to onset of winter. Larvae terminate diapause shortly after spring snow melt (late May to mid-June); most larvae diapause a second winter as L5 before pupating. L5 instars move away from host plants and pupate within 50 cm of the ground; pupation to adult emergence requires about 21 days (Williams 1981; Williams et al. 1984). Males patrol near conifer tree tops in search of females, and mating typically occurs in or near the tops of trees.
- Literature Cited AboveLegend: View Online Publication
- Debinski, D. 1993. Butterflies of Glacier National Park, Montana. Occasional Papers of the Museum of Natural History, the University of Kansas, Lawrence, Kansas. No. 159: 1-13.
- Ferris, C.D. and F.M. Brown (eds). 1981. Butterflies of the Rocky Mountains. Univ. of Oklahoma Press. Norman. 442 pp.
- Glassberg, J. 2001. Butterflies through Binoculars: A Field Guide to the Butterflies of Western North America. Oxford University Press.
- Guppy, C.S. and J.H. Shepard. 2001. Butterflies of British Columbia: including western Alberta, southern Yukon, the Alaska Panhandle, Washington, northern Oregon, northern Idaho, northwestern Montana. UBC Press (Vancouver, BC) and Royal British Columbia Museum (Victoria, BC). 414 pp.
- Kohler, S. 1980. Checklist of Montana Butterflies (Rhopalocera). Journal of the Lepidopterists' Society 34(1): 1-19.
- Pyle, R.M. 2002. The butterflies of Cascadia: a field guide to all the species of Washington, Oregon, and surrounding territories. Seattle Audubon Society, Seattle, Washington. 420 pp.
- Scott, J.A. 1986. The butterflies of North America: a natural history and field guide. Stanford University Press, Stanford, California.
- Scott, J.A. 2014. Lepidoptera of North America 13. Flower visitation by Colorado butterflies (40,615 records) with a review of the literature on pollination of Colorado plants and butterfly attraction (Lepidoptera: Hersperioidea and Papilionoidea). Contributions of the C.P. Gillette Museum of Arthopod Diversity. Fort Collins, CO: Colorado State University. 190 p.
- Stanford, R.E. and P.A. Opler. 1993. Atlas of western USA butterflies: including adjacent parts of Canada and Mexico. Unpubl. Report. Denver and Fort Collins, Colorado 275 pp.
- Williams, E.H. 1981. Thermal influences on oviposition in the montane butterfly Euphydryas gillettii. Oecologia 50(3): 342-346.
- Williams, E.H. 1988. Habitat and range of Euphydryas gillettii (Nymphalidae). Journal of the Lepidopterists' Society 42(1): 37-45.
- Williams, E.H. 1995. Fire-Burned Habitat and Reintroduction of the Butterfly Euphydryas Gillettii (Nymphalidae). Journal of the Lepidopterists' Society 49: 183-191.
- Williams, E.H. and M.D. Bowers. 1987. Factors Affecting Host Plant Use by the Montane Butterfly Euphydryas Gillettii (Nymphalidae). American Midland Naturalist 118(1): 153-161.
- Williams, E.H., C.E. Holdren, and P.R. Ehrlich. 1984. The Life History and Ecology of Euphydryas Gillettii Barnes (Nymphalidae). Journal of the Lepidopterists' Society 38(1): 1-12.
- Additional ReferencesLegend: View Online Publication
Do you know of a citation we're missing?
- Allen, T.J., J.P. Brock, and J. Glassberg. 2005. Caterpillars in the field and garden: a field guide to the butterfly caterpillars of North America. Oxford University Press.
- Brock, J.P. and K. Kaufman. 2003. Kaufman Field Guide to Butterflies of North America. Houghton Mifflin Company, New York, NY 284 pp.
- Layberry, R.A., P.W. Hall, and J.D. LaFontaine. 1998. The Butterflies of Canada. University of Toronto Press. 280 pp. + color plates.
- Opler, P.A. and A.B. Wright. 1999. A field guide to western butterflies. Second edition. Peterson Field Guides. Houghton Mifflin Company, Boston, Massachusetts. 540 pp.
- Additional Sources of Information Related to "Insects"