Fig. 1 in Can biogeography help bumblebee conservation?
Fig. 1. Revising bumblebee species world-wide. The total bumblebee (indigenous) species richness is highest in Asia, especially in the Himalaya and Hengduan Mountains on the southern and eastern fringes of the Qinghai-Tibetan Plateau (Williams 1998, data updated). There are no indigenous bumblebees...
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ftzenodo:oai:zenodo.org:8305617 2023-10-01T03:51:04+02:00 Fig. 1 in Can biogeography help bumblebee conservation? Williams, Paul H. 2023-08-30 https://zenodo.org/record/8305617 https://doi.org/10.5281/zenodo.8305617 unknown doi:10.5852/ejt.2023.890.2259 lsid:urn:lsid:plazi.org:pub:FFE8FFE7FF8D5573CF653D79F77DFFCA https://zenodo.org/record/8305615 doi:10.5281/zenodo.8305616 https://zenodo.org/communities/biosyslit https://zenodo.org/record/8305617 https://doi.org/10.5281/zenodo.8305617 oai:zenodo.org:8305617 info:eu-repo/semantics/openAccess https://creativecommons.org/licenses/by/4.0/legalcode European Journal of Taxonomy 890(1) 165-183 Biodiversity Taxonomy info:eu-repo/semantics/other image-figure 2023 ftzenodo https://doi.org/10.5281/zenodo.830561710.5852/ejt.2023.890.225910.5281/zenodo.8305616 2023-09-05T22:58:36Z Fig. 1. Revising bumblebee species world-wide. The total bumblebee (indigenous) species richness is highest in Asia, especially in the Himalaya and Hengduan Mountains on the southern and eastern fringes of the Qinghai-Tibetan Plateau (Williams 1998, data updated). There are no indigenous bumblebees in sub-Saharan Africa, lowland India, or in Australia and New Zealand (and Antarctica). Species numbers peak in the region of Xining, Qinghai. Even when mapping such a globally well-sampled group as bumblebees, using a coarse-scale equal-area grid reduces species-area effects, reduces the effects of sampling heterogeneity (species-accumulation curves for these large grid cells are more nearly asymptotic than for many smaller grid cells), and smooths the effects of local habitat variation. The grid is based on intervals of 10° longitude, which are used to calculate graduated latitudinal intervals so as to provide equal-area cells (each cell has an area of approximately 611 000 km²). The colour scale has equal-frequency richness classes. Cylindrical orthomorphic equal-area projection (excluding Antarctica) with north at the top of the map. Lower left, inset: field-work sites sampled for bumblebees by the author 1971–2018 (red spots). Published as part of Williams, Paul H., 2023, Can biogeography help bumblebee conservation?, pp. 165-183 in European Journal of Taxonomy 890 (1) on page 167, DOI:10.5852/ejt.2023.890.2259, http://zenodo.org/record/8305615 Still Image Antarc* Antarctica Zenodo New Zealand |
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Biodiversity Taxonomy |
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Biodiversity Taxonomy Williams, Paul H. Fig. 1 in Can biogeography help bumblebee conservation? |
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Biodiversity Taxonomy |
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Fig. 1. Revising bumblebee species world-wide. The total bumblebee (indigenous) species richness is highest in Asia, especially in the Himalaya and Hengduan Mountains on the southern and eastern fringes of the Qinghai-Tibetan Plateau (Williams 1998, data updated). There are no indigenous bumblebees in sub-Saharan Africa, lowland India, or in Australia and New Zealand (and Antarctica). Species numbers peak in the region of Xining, Qinghai. Even when mapping such a globally well-sampled group as bumblebees, using a coarse-scale equal-area grid reduces species-area effects, reduces the effects of sampling heterogeneity (species-accumulation curves for these large grid cells are more nearly asymptotic than for many smaller grid cells), and smooths the effects of local habitat variation. The grid is based on intervals of 10° longitude, which are used to calculate graduated latitudinal intervals so as to provide equal-area cells (each cell has an area of approximately 611 000 km²). The colour scale has equal-frequency richness classes. Cylindrical orthomorphic equal-area projection (excluding Antarctica) with north at the top of the map. Lower left, inset: field-work sites sampled for bumblebees by the author 1971–2018 (red spots). Published as part of Williams, Paul H., 2023, Can biogeography help bumblebee conservation?, pp. 165-183 in European Journal of Taxonomy 890 (1) on page 167, DOI:10.5852/ejt.2023.890.2259, http://zenodo.org/record/8305615 |
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Still Image |
author |
Williams, Paul H. |
author_facet |
Williams, Paul H. |
author_sort |
Williams, Paul H. |
title |
Fig. 1 in Can biogeography help bumblebee conservation? |
title_short |
Fig. 1 in Can biogeography help bumblebee conservation? |
title_full |
Fig. 1 in Can biogeography help bumblebee conservation? |
title_fullStr |
Fig. 1 in Can biogeography help bumblebee conservation? |
title_full_unstemmed |
Fig. 1 in Can biogeography help bumblebee conservation? |
title_sort |
fig. 1 in can biogeography help bumblebee conservation? |
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2023 |
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https://zenodo.org/record/8305617 https://doi.org/10.5281/zenodo.8305617 |
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New Zealand |
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New Zealand |
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Antarc* Antarctica |
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Antarc* Antarctica |
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European Journal of Taxonomy 890(1) 165-183 |
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doi:10.5852/ejt.2023.890.2259 lsid:urn:lsid:plazi.org:pub:FFE8FFE7FF8D5573CF653D79F77DFFCA https://zenodo.org/record/8305615 doi:10.5281/zenodo.8305616 https://zenodo.org/communities/biosyslit https://zenodo.org/record/8305617 https://doi.org/10.5281/zenodo.8305617 oai:zenodo.org:8305617 |
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info:eu-repo/semantics/openAccess https://creativecommons.org/licenses/by/4.0/legalcode |
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https://doi.org/10.5281/zenodo.830561710.5852/ejt.2023.890.225910.5281/zenodo.8305616 |
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