Vancouver Bumble Bee - Bombus vancouverensis
For definitions and diagrams of bumble bee morphology please see the Montana State Entomology Collection's Bumble Bee Morphology page
. [Formerly classified as B. bifarius, now considered B. vancouverensis nearctica in Montana.] A medium-tongued, small-sized bumble bee: queens 15-19 mm in length, workers 8-14 mm. Head medium length, cheek just shorter than wide; mid leg basitarsus back far corner rounded, outer surface of hind leg tibia concave and hairless (except fringe) forming pollen basket; hair on face yellow or white, sometimes with many black hairs intermixed on upper side of head; yellow or white hairs of thorax anterior to wings sometimes intermixed with black, giving a cloudy appearance; wide black wedge of black hairs projects posteriorly on thorax to back edge; sides of thorax with black hairs in at least the lower third; hind leg fringes of pollen basket pale orangy-brown, or if T3 black then fringe may be black; T1 yellow or white, T2 usually with a patch of black hair in front middle (although T2-3 may show partial or complete replacement of red hairs with black), T4 yellow, T5 black with yellow only on extreme side and back fringes. Males 8-13 mm in length; eyes similar in size and shape to eyes of any female bumble bee; antennae medium length, flagellum 3X longer than scape; hair color pattern similar to queens and workers, occasionally T1-2 and T4-5 mostly yellow, T3 and T6 mostly black (Koch et al. 2012, Williams et al. 2014).
Across the range, queens reported March to September, workers April to October, males May to October (Williams et al. 2014). In Utah, queens and workers reported March to September, males July to September (Koch et al. 2012); in California, queens early March to late October, workers early April to early October, males early June to early October (Thorp et al. 1983).
Please see the Montana State Entomology Collection's Key to Female Bumble Bees in Montana
. [Former B. bifarius now considered this species in Montana.] Females told from other Montana Bombus
by a combination of outer surface of hind leg tibia concave and hairless (except fringe) forming a pollen basket; pollen basket fringe orange or brown; exoskeleton of hind leg basitarsus brownish orange and often lighter than tibia; scutum anterior to wings with yellow and black hairs intermixed, giving a cloudy appearance; T2-3 with red or orange hairs, T2 with black hairs at least in middle.
Resident Year Round
Recorded Montana Distribution
Click the map for additional distribution information.
[Former B. bifarius now considered this species in Montana.] Throughout the mountain west from southern Alaska to the Mexican border, east to the Black Hills of South Dakota and western Great Plains (Koch et al. 2012, Williams et al. 2014). In Colorado from 1600-4200 m elevation with peak abundance 2400-2900 m (Macior 1974). In California, from near sea level to at least 3655 m elevation (Thorp et al. 1983). In Montana, to at least 3050 m elevation in the Beartooth Mountains (Bauer 1983). Considered common to very common in most of its range (Cameron et al. 2011, Koch et al. 2012, Williams et al 2014).
Prairie, grassland, riparian woodland, sagebrush steppe, chaparral, urban parks and gardens, mountain meadows to above treeline in alpine tundra (Hobbs 1967, Macior 1974, Bauer 1983, McFrederick and LeBuhn 2006, Cook et al. 2011, Williams et al. 2014). Abundance in sagebrush steppe tends to be inversely related to percent canopy cover of sagebrush (Cook et al. 2011).
Feeds on a variety of flowers, including Achillea, Agoseris, Allium, Anaphalis, Arctostaphylos, Arnica, Artemisia, Astragalus, Castilleja, Ceanothus, Centaurea, Chionophila, Chrysopsis, Chrysothamnus, Cichorium, Cirsium, Collinsia, Convolvulus, Corydalis, Dodecatheon, Epilobium, Ericameria, Erigeron, Eriogonum, Erysimum, Eupatorium, Frasera, Geranium, Grindelia, Haplopappus, Helenium, Iris, Linaria, Linum, Lupinus, Melilotus, Mentha, Mertensia, Microseris, Mimulus, Nama, Onosmodium, Orthocarpus, Oxytropis, Pedicularis, Penstemon, Phacelia, Polemonium, Polygonum, Potentilla, Primula, Prunus, Ranunculus, Rhus, Ribes, Rubus, Rudbeckia, Salix, Salvia, Sanicula, Sedum, Senecio, Sisymbrium, Sisyrinchium, Solidago, Sonchus, Symphoricarpos, Symphyotrichum, Tanacetum, Taraxacum, Thermopsis, Trifolium, Vicia and Viguiera (Beattie et al. 1973, Macior 1974, Schmitt 1980, Thorp et al. 1983, Bauer 1983, Mayer et al. 2000, Wilson et al. 2010, Koch et al. 2012, Pyke et al. 2012, Miller-Struttmann and Galen 2014, Williams et al. 2014).
Nests usually built underground, but sometimes on ground surface (Williams et al. 2014). In southern Alberta, 82.4% of 188 nests were built underground. Nests initiated late May to early July, with most begun by mid June; nest entrances often camouflaged (Hobbs 1967, Richards 1978). Mean numbers of eggs, larvae and pupae, respectively, of first broods are 8.7, 8.9 and 8.5. Mean number of eggs laid per cell in second and thirds broods is 3.8. Males patrol circuits in search of queens. Queens apparently mate only once. Queens hibernate in the ground at an average depth of 10.4 cm but up to at least 18 cm. (Hobbs 1967).
- Literature Cited AboveLegend: View Online Publication
- Bauer, P.J. 1983. Bumblebee pollination relationships on the Beartooth Plateau tundra of Southern Montana. American Journal of Botany. 70(1): 134-144.
- Beattie, A.J., D.E. Breedlove, and P.R. Ehrlich. 1973. The ecology of the pollinators and predators of Frasera speciosa. Ecology 54: 81-91.
- Cook, S.P., S.A. Birch, F.W. Merickel, C.C. Lowe, and D. Page-Dumroese. 2011. Bumble bee (Hymenoptera: Apidae) community structure on two sagebrush steppe sites in southern Idaho. Pan-Pacific Entomologist 87(3): 161-171.
- Hobbs, G.A. 1967. Ecology of species of Bombus Latr. (Hymenoptera: Apidae) in southern Alberta. VI. Subgenus Pyrobombus. Canadian Entomologist 99: 1271-1292.
- Kearns, C.A. and J.D. Thomson. 2001. The Natural History of Bumble Bees. Boulder, CO. University Press of Colorado.
- Koch, J., J. Strange, and P. Williams. 2012. Bumble bees of the western United States. Washington, DC: USDA Forest Service, Pollinator Partnership. 143 p.
- Macior, L.M. 1974. Pollination ecology of the Front Range of the Colorado Rocky Mountains. Melanderia 15: 1-59.
- Mayer, D.F., E.R. Miliczky, B.F. Finnigan, and C.A. Johnson. 2000. The bee fauna (Hymenoptera: Apoidea) of southeastern Washington. Journal of the Entomological Society of British Columbia 97: 25-31.
- McFrederick, Q.S. and G. LeBuhn. 2006. Are urban parks refuges for bumble bees Bombus spp. (Hymenoptera: Apidae)? Biological Conservation 129: 372-382.
- Miller-Struttmann, N.E. and C. Galen. 2014. High-altitude multi-taskers: bumble bee food plant use broadens along an altitudinal productivity gradient. Oecologia 176:1033-1045.
- Pyke, G.H., D.W. Inouye, and J.D. Thomson. 2012. Local geographic distributions of bumble bees near Crested Butte, Colorado: competition and community structure revisited. Environmental Entomology 41(6): 1332-1349.
- Richards, K.W. 1978. Nest site selection by bumble bees (Hymenoptera: Apidae) in southern Alberta. Canadian Entomologist 110(3): 301-318.
- Schmitt, J. 1980. Pollinator foraging behavior and gene dispersal in Senecio (Compositae). Evolution 34: 934-943.
- Thorp, R.W., D.S. Horning, and L.L. Dunning. 1983. Bumble bees and cuckoo bumble bees of California (Hymenoptera: Apidae). Bulletin of the California Insect Survey 23:1-79.
- Williams, P., R. Thorp, L. Richardson, and S. Colla. 2014. Bumble Bees of North America. Princeton, NJ: Princeton University Press. 208 p.
- Wilson, J.S., L.E. Wilson, L.D. Loftis, and T. Griswold. 2010. The montane bee fauna of north central Washington, USA, with floral associations. Western North American Naturalist 70(2): 198-207.
- Additional ReferencesLegend: View Online Publication
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- Burkle L.A., M.P. Simanonok, J.S. Durney, J.A. Myers, and R.T. Belote. 2019. Wildfires influence abundance, diversity, and intraspecific and interspecific trait variation of native bees and flowering plants across burned and unburned landscapes. Frontiers in Ecology and Evolution 7(252):1-14.
- Cameron, S.A., J.D. Lozier, J.P. Strange, J.B. Koch, N. Cordes, L.F. Solter, and T.L. Griswold. 2011. Patterns of widespread decline in North American bumble bees. Proceedings of the National Academy of Sciences 108(2): 662-667.
- Delphia, C.M., Griswold, T., Reese, E.G., O'Neill, K.M., and Burkle, L.A. 2019. Checklist of bees (Hymenoptera: Apoidea) from small, diversified vegetable farms in south-western Montana. Biodiversity Data Journal: e30062
- Dolan, A.C. 2016. Insects associated with Montana's huckleberry (Ericaceae: Vaccinium globulare) plants and the bumble bees (Hymenoptera: Apidae) of Montana. M.Sc. Thesis. Bozeman, MT: Montana State University. 160 p.
- Dolan, A.C., C.M. Delphia, K.M. O'Neill, and M.A. Ivie. 2017. Bumble Bees (Hymenoptera: Apidae) of Montana. Annals of the Entomological Society of America. 110(2): 129-144.
- Reese, E.G., L.A. Burkle, C.M. Delphia, and T. Griswold. 2018. A list of bees from three locations in the Northern Rockies Ecoregion (NRE) of western Montana. Biodiversity Data Journal 6: e27161.
- Simanonok, M. 2018. Plant-pollinator network assembly after wildfire. Ph.D. Dissertation. Bozeman, MT: Montana State University. 123 p.
- Simanonok, M.P. and L.A. Burkle. 2019. Nesting success of wood-cavity-nesting bees declines with increasing time since wildfire. Ecology and Evolution 9:12436-12445.
- Simanonok, M.P., and L.A. Burkle. 2014. Partitioning interaction turnover among alpine pollination networks: Spatial temporal, and environmental patterns. Ecosphere 5(11):149.
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