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dc.contributor.authorBecher, M
dc.contributor.authorTwiston-Davies, G
dc.contributor.authorOsborne, J
dc.contributor.authorLander, T
dc.date.accessioned2024-03-11T10:41:09Z
dc.date.issued2024-03-11
dc.date.updated2024-03-07T17:02:47Z
dc.description.abstractAbstract of associated paper: 1. A common management intervention to support declining wild pollinators is ‘pollinator planting’. However, despite years of inclusion in conservation initiatives, global pollinator declines continue. 2. Using the agent-based model BEE-STEWARD with two example species, Bombus terrestris and B. pascuorum, we explore when during the year bumblebee resource demand is highest, and how that relates to seasonal changes in colony composition (numbers of eggs, larvae, pupae, and adults). We then examine the impact of two-week periods of resource scarcity across the year. Finally, we explore how enhancement with early-spring-blooming herbaceous species or trees changes colony survival and queen production. 3. In the UK there is a previously under-appreciated ‘hungry gap’ for bumblebees in March-April, before the peak flight period, driven by the resource demands of larvae for protein and thermoregulation in the colony, rather than the number of adult bees. 4. A 2-week gap in forage availability during this period drives a 50-87% drop in queen the production of daughter queens for the following year. Adding early blooming species in the model had significant, positive, long-term effects on colony survival probability and daughter queen production. 5. Pollinator planting initiatives in both national and international conservation schemes need to include plants that flower up to one month before the adults of target social pollinator species are apparent in the field, during the period that larvae dominate the colony. This approach is likely to increase colony survival and queen production, contributing towards halting and reversing global pollinator decline.en_GB
dc.description.sponsorshipNatural Environment Research Council (NERC)en_GB
dc.description.sponsorshipNatural Environment Research Council (NERC)en_GB
dc.description.sponsorshipLeverhulme Trusten_GB
dc.description.sponsorshipHalpin Trusten_GB
dc.format.zip .docx .txt .xls .csv .png .nlogo
dc.identifier.doi10.24378/exe.5047
dc.identifier.grantnumberNE/P016731/1en_GB
dc.identifier.grantnumberNE/P011217/1en_GB
dc.identifier.grantnumberECF-2013-090en_GB
dc.identifier.urihttp://hdl.handle.net/10871/135522
dc.identifierORCID: 0000-0002-9937-172X (Osborne, Juliet)
dc.language.isoenen_GB
dc.publisherUniversity of Exeteren_GB
dc.relation.urlhttp://hdl.handle.net/10871/135532en_GB
dc.rightsCC BY 4.0en_GB
dc.subjectagent-based modelen_GB
dc.subjectBee-stewarden_GB
dc.subjectforagingen_GB
dc.subjectnectaren_GB
dc.subjectpollenen_GB
dc.subjectpollinator plantingen_GB
dc.subjectagent-based modelen_GB
dc.subjectbee-stewarden_GB
dc.subjectforagingen_GB
dc.subjectnectaren_GB
dc.subjectpollenen_GB
dc.subjectpollinator plantingen_GB
dc.titleResource gaps pose the greatest threat for bumblebees during the colony establishment phase (dataset)en_GB
dc.typeDataseten_GB
dc.date.available2024-03-11T10:41:09Z
dc.descriptionThis dataset (in a zipped folder) contains the modified version of the BEESTEWARD model used in the above paper. Definitions of the simulation experiments are given and all necessary input files are provided to re-run the simulations presented in the manuscript. Further details are given in the ReadMe file. The model is implemented in Netlogo (5.3.1) which can be downloaded here: https://ccl.northwestern.edu/netlogo/5.3.1/en_GB
dc.descriptionThe article associated with this dataset is available in ORE at: http://hdl.handle.net/10871/135532en_GB
dc.identifier.journalInsect Conservation and Diversityen_GB
dc.rights.urihttps://creativecommons.org/licenses/by/4.0en_GB
rioxxterms.versionNAen_GB
rioxxterms.licenseref.startdate2024-03-11
rioxxterms.typeOtheren_GB
refterms.dateFOA2024-03-11T10:41:16Z


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