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142 results for “pollinator community”

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zenodo32/100

Figure 12 in Community-level plant-pollinator interactions in a Palaeotropical montane evergreen oak forest ecosystem

Figure 12. Flowers visited by thrips and bugs. (a, b) Chloranthus nervosus visited by thrips; (c) Mytilaria laosensis visited by thrips; (d, e) Dioscorea bulbifera visited by thrips; (f) Maesa sp., visited by a mecopteran; (g) Elatostema involucratum visited by a mirid bug; (h) Elatostema balansae visited by a mirid bug.

opennotspecifiedFeb 2021View details →
zenodo32/100

Figure 10 in Community-level plant-pollinator interactions in a Palaeotropical montane evergreen oak forest ecosystem

Figure 10. Flowers visited by beetles. (a, b) Fissistigma cupreonitens visited by chrysomelid beetles, an inner petal removed to show the inner chamber in (b); (c) Gentiana zollingeri visited by a scarabaeid beetle; (d) Melastoma malabathrica visited by scarabaeid beetles; (e) Photinia prunifolia visited by a scarabaeid beetle; (f) Lithocarpus elegans visited by a cerambycid beetle; (g) Euodia lepta visited by cerambycid beetles; (h) Photinia prunifolia visited by a cerambycid beetle; (i) Melastoma malabathrica visited by a meloid beetle, Mylabris phalerata; (j) Lithocarpus mucronata visited by a dermatid beetle; (k) Vitex leptobotrys visited by a curculionid beetle.

opennotspecifiedFeb 2021View details →
zenodo32/100

Figure 8 in Community-level plant-pollinator interactions in a Palaeotropical montane evergreen oak forest ecosystem

Figure 8. Flowers visited by small bees and wasps. (a) Embelia ribes visited by a stingless bee; (b) Thladiantha sp. visited by Ctenoplectra cornuta (visitor not in the photo); (c) Uncaria scandens visited by a halictid bee; (d) Sterculia henryi visited by a halictid bee; (e) Ludwigia hyssopifolia visited by a halictid bee; (f) Lysimachia siamensis visited by a Macropis orientalis bee; (g) Baliospermum montanum visited by a scoliid wasp; (h) Euphorbia lathyris visited by an ant; (i) Euodia lepta visited by an eumenid wasp; (j) Cynoglossum zeylanicum visited by an eumenid wasp; (k) Photinia prunifolia visited by an eumenid wasp.

opennotspecifiedFeb 2021View details →
zenodo32/100

Figure 2 in Community-level plant-pollinator interactions in a Palaeotropical montane evergreen oak forest ecosystem

Figure 2. Seasonal changes in monthly temperature (averages of monthly maximum, mean and minimum) and rainfall at Xam Neua near S4.

opennotspecifiedFeb 2021View details →
zenodo32/100

Figure 6 in Community-level plant-pollinator interactions in a Palaeotropical montane evergreen oak forest ecosystem

Figure 6. Flowers visited by honeybees: A. laboriosa (a–c), A. dorsata (d–f), Apis cerana (g–k) and A. florea (l). (a) Castanopsis diversifolia; (b) Castanopsis diversifolia; (c) Rubus multibracteatus; (d) Stachytarpheta jamaicensis; (E) Symplocos ramosissima; (f) Pogostemon nelsonii; (g) Ageratum houstonianum; (h) Photinia prunifolia; (i) Rubus obcordatus; (j) Bidens pilosa var. radiata; (k) Ixeris gracilis; (l) Photinia prunifolia.

opennotspecifiedFeb 2021View details →
zenodo32/100

Figure 3 in Community-level plant-pollinator interactions in a Palaeotropical montane evergreen oak forest ecosystem

Figure 3. Landscapes of the study sites S1–S5. (a) a meadow at S1; (b) paddy fields and secondary deciduous forests at S2; (c) a subtropical evergreen forest at S3; (d) a landscape at S4; (e) a valley inhabited by several Impatiens species at S4; (f) an evergreen oak forest near the summit of a mountain at S4; (g) a riverine forest inhabited by Mytilaria laosensis at S4; (h) limestone hills at S5.

opennotspecifiedFeb 2021View details →
zenodo32/100

Figure 11 in Community-level plant-pollinator interactions in a Palaeotropical montane evergreen oak forest ecosystem

Figure 11. Flowers visited by lepidopterans. (a) Isodon glaucocalyx visited by papilionid butterfly Papilio polytes; (b) Barleria cristata visited by a papilionid butterfly Papilio protenor; (c) Mussaenda cambodiana visited by a papilionid butterfly Troides helena; (d) Baliospermum montanum visited by a lycaenid butterfly Heliophorus epicles; (e) Lindera tonkinensis visited by a lycaenid butterfly Pithecos corbus; (f) Blumea martiniana visited by a nymphalid butterfly Zemeros flegyas; (g) Lindera tonkinensis visited by a nymphalid butterfly Yptima confusa; (h) Impatiens violaeflora visited by a hesperiid butterfly Onryza siamica; (i) Pottsia laxiflora visited by a pierid butterfly Appias albina; (j) Swertia aungustifolia visited by an arctiid moth and a hovering blue-banded Amegilla bee; (k) Ligustrum indicum visited by an arctiid moth.

opennotspecifiedFeb 2021View details →
zenodo32/100

Figure 16 in Community-level plant-pollinator interactions in a Palaeotropical montane evergreen oak forest ecosystem

Figure 16. The observed plant–pollinator network between flowers and eight groups of long-tongued bees. See Table 2 for plant species codes.

opennotspecifiedFeb 2021View details →
zenodo32/100

Figure 15 in Community-level plant-pollinator interactions in a Palaeotropical montane evergreen oak forest ecosystem

Figure 15. Flowers of eight observed Impatiens species (Bal1–Bal8): (a) I. chinensis; (b) I. commellinoides; (c) I. ernestii; (d) I. longiloba; (e) I. mengtszeana; (f) I. rubricolor; (g) I. tigrina; (h) I. violaeflora.

opennotspecifiedFeb 2021View details →
zenodo32/100

Figure 18 in Community-level plant-pollinator interactions in a Palaeotropical montane evergreen oak forest ecosystem

Figure 18. Comparison of pollination systems among climatic and geographical regions: subalpine forests and meadows at Mt. Kushigata, central Japan (Kato 2000; Kato et al. 1993b), cool temperate deciduous forests at Ashu (Kato et al. 1990), warm temperate evergreen forest ecosystem at Amami Island (Kato 2000), montane evergreen forests in Laos (this paper), tropical monsoon forest ecosystem at lowland Laos (Kato et al. 2008), Bornean tropical rain forests at Lambir Hills National Park in Malaysia (Momose et al. 1998), and a Neotropical rain forest at La Selva (Kress and Beach 1994). The asterisk denotes large bees including long-tongued bees and carpenter bees.

opennotspecifiedFeb 2021View details →
dryad32/100

Pollinator community and generalisation of pollinator spectra changes with plant niche width and local dominance

<p>Floral traits are assumed to be the main determinants of plants' pollinator spectrum, yet a majority of temperate plant species possess traits allowing for a certain degree of generalisation of their pollinator spectrum. The actual level of pollinator spectrum generalisation is likely to be the result of both plant floral traits and the diversity and abundance of plant species a plant co-occurs with. We expect that plant species co-occurring in highly diverse plant communities should host more generalised pollinator spectra. In the present study, we explore the degree to which the composition and generalisation of plant-pollinator spectra depend on the plant's niche width (measured as co-occurrence with other plant species) and its local dominance (as measured by mean cover in the community). For this purpose, we compiled a database of &gt;250 plant species pollinator spectra from the literature and coupled it with data on plant niche width and local dominance based on the Czech National Phytosociological Database. Species with wider niches had on average more generalised pollinator spectra, ranging from bumblebee-dominated spectra to Diptera- and/or nitidulid beetle-dominated spectra, which was strongly related to plant phylogeny. Plants with bumblebee-dominated spectra had neither wide nor narrow niches. The majority of plants had either muscid-, hoverfly- or nitidulid-dominated or completely generalised pollinator spectra. Among such plants, higher local dominance increased the proportion of opportune muscids in pollinator spectrum, while hoverflies showed the opposite pattern. Honeybees although rather infrequent in pollinator spectra also showed a strong response to locally dominant plant species.</p> <p><em>Synthesis</em>: The composition of a plant's pollinator spectrum is not independent of other aspects of the plant's life-history, namely, niche width and the ability to dominate the community. Wider plant species niches result in more generalised pollinator spectra, supporting our hypothesis that habitat generalists are less prone to specialisation on particular pollinator groups. Conversely, the ability to dominate local plant communities influenced pollinator spectra mainly through specific responses of individual pollinator groups.</p>

opencc-zeroJul 2023View details →
dryad32/100

Data from: Spatial variability in a plant-pollinator community across a continuous habitat: high heterogeneity in the face of apparent uniformity

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publicJun 2019View details →
dryad32/100

Influence of climate, weather and floral associations on pollinator community composition across an elevational gradient

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publicOct 2024View details →
dryad32/100

Data from: Constructing more informative plant-pollinator networks: visitation and pollen deposition networks in a heathland plant community

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publicAug 2015View details →
dryad32/100

Data from: Taxonomic and functional diversity of the co-flowering community differentially affect Cakile edentula pollination at different spatial scales

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publicApr 2019View details →
dryad32/100

Data from: Floral volatiles structure plant-pollinator interactions in a diverse community across the growing season

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publicAug 2019View details →
dryad32/100

Data from: Inferring processes of coevolutionary diversification in a community of Panamanian strangler figs and associated pollinating wasps

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publicJul 2019View details →
dryad32/100

Low host specificity and broad geographic ranges in a community of parasitic non-pollinating fig wasps (Sycoryctinae; Chalcidoidea)

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publicMar 2021View details →
dryad32/100

Data from: Associations between plant and pollinator communities under grassland restoration respond mainly to landscape connectivity

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publicJun 2019View details →
dryad32/100

Data from: Local adaptation: mechanical fit between floral ecotypes of Nerine humilis (Amaryllidaceae) and pollinator communities

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publicJul 2015View details →

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International Brain Laboratory public data

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