Bombus (Thoracobombus) pensylvanicus (De Geer)
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https://doi.org/ 10.17161/jom.v0i50.4834 |
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https://treatment.plazi.org/id/4A7B7945-FFA3-EB5A-9AE3-372D0F52F828 |
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Felipe |
scientific name |
Bombus (Thoracobombus) pensylvanicus (De Geer) |
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Bombus (Thoracobombus) pensylvanicus (De Geer) View in CoL
‘American Bumble Bee’
Bombus pensylvanicus View in CoL [as B. americanorum (Fabricius) View in CoL ] was listed as the “most widespread and common species” in the state in Chandler & McCoy’s (1965) study. Its statewide occurrence is much reduced today, although it remains widespread ( Fig. 1). The contemporary occurrence of B. pensylvanicus View in CoL (50%) is about one-third lower than its historic occurrence (82%, Fig. 3). Only a single record occurred in the period between our sampling intervals: Faulkner Co., September 6, 1976. This state-level pattern reflects what has also been observed throughout the range of B. pensylvanicus View in CoL , and many sources consider B. pensylvanicus View in CoL to be a declining species ( Cameron et al., 2011; Colla & Packer, 2008; Colla et al., 2012; Grixti et al., 2009). Although there are indications of a range-wide decline of B. pensylvanicus View in CoL , it is likely that not all areas are reflecting the same shifts in abundance or occurrence. For example, B. pensylvanicus View in CoL was abundant in the extreme south and western portions of its range (Louisiana, Oklahoma, and Texas) in recent surveys, although it was absent from much of the northern and eastern areas in which it was expected to occur ( Cameron et al., 2011). Similarly, B. pensylvanicus View in CoL was absent from the northern region of Illinois in recent surveys, although it was known from northern Illinois in historical records ( Grixti et al., 2009). With contemporary records occurring throughout the state and in each ecoregion, we found no geographic pattern in the occurrences of B. pensylvanicus View in CoL within Arkansas. This heterogeneity among regional studies highlights the utility of localized studies in determining the conservation status of species of interest.
GLOSSA LENGTH: Long (6.41 ± 0.58 mm).
ADULT ACTIVE PERIOD: Late season with a long active period (82 days). Majority: late June through mid-September; Earliest: May 13; Latest: October 16.
PREFERRED PLANTS: Baptisia alba (wild white indigo, Fabaceae ), Vernonia Schreb. (ironweed, Asteraceae ), T. canadense ( Canada germander, Lamiaceae ), M. fistulosa (wild bergamot, Lamiaceae ), A. esculentus (okra, Malvaceae ), Solanum carolinense Linnaeus (Carolina horsenettle, Solanaceae ), Cirsium discolor (Muhl. ex Willd.) Spreng. (field thistle, Asteraceae ), S. azurea (azure blue sage, Lamiaceae ), S. integrifolium (wholeleaf rosinweed, Asteraceae ), V. villosa (winter vetch, Fabaceae ).
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