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Biogeography and designatable units of <Emphasis Type="Italic">Bombus occidentalis</Emphasis> Greene and <Emphasis Type="Italic">B. terricola</Emphasis> Kirby (Hymenoptera: Apidae) with implications for conservation status assessments
Authors:Cory S Sheffield  Leif Richardson  Syd Cannings  Hien Ngo  Jennifer Heron  Paul H Williams
Institution:1.Royal Saskatchewan Museum,Regina,Canada;2.Gund Institute for Ecological Economics,University of Vermont,Burlington,USA;3.Canadian Wildlife Service,Environment Canada,Whitehorse,Canada;4.Department of Biology,York University,Toronto,Canada;5.Species Conservation Science Unit,British Columbia Ministry of Environment,Vancouver,Canada;6.Department of Life Sciences,The Natural History Museum,London,UK
Abstract:Conservation action for species of concern requires that “designatable units” (e.g., species, subspecies, geographic races, genetically distinct forms) are clearly defined, or that the species complex is treated as a whole. Several species of bumble bee are currently threatened, and some of these have cryptic colouration (resembling other species), or form complexes that vary considerably in colour patterning. Here we address the taxonomy and distribution of Bombus occidentalis Greene and B. terricola Kirby, both of which are currently of conservation concern in North America. Bombus occidentalis includes two apparently monophyletic groups of COI barcode haplotypes (recently considered as subspecies) with ranges mostly separated by that of their sister species, B. terricola. The southern B. o. occidentalis ranges throughout the western United States and into western Canada from southern Saskatchewan and Alberta, and throughout British Columbia north to ca. 55°N; the northern B. o. mckayi Ashmead, is restricted to north of this in British Columbia, westernmost Northwest Territories, Yukon Territory and Alaska. Bombus o. mckayi exists, as far as is known, only with a “banded” colour pattern. By contrast, B. o. occidentalis occurs in both banded and non-banded colour patterns, although the southern banded colour pattern is geographically isolated from the northern subspecies. Bombus o. occidentalis has declined throughout its range, perhaps due in part to exposure to novel parasites. Despite having similar levels of parasitism (ca. 40 %) as the southern subspecies, B. o. mckayi appears to have stable populations at present. There is therefore compelling evidence that the two subspecies should be distinguished for conservation and management purposes. We present the evidence for their distinction and provide tools for subspecies recognition.
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