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Tree invasions have substantial impacts on biodiversity and ecosystem functioning, and trees that are dispersed by animals are more likely to become invasive. In addition, hybridisation between plants is well documented as a source of new weeds, as hybrids gain new characteristics that allow them to become invasive. Corymbia torelliana is an invasive tree with an unusual animal dispersal mechanism: seed dispersal by stingless bees, that hybridizes readily with other species. We examined hybrids between C. torelliana and C. citriodora subsp. citriodora to determine whether hybrids have inherited the seed dispersal characteristics of C. torelliana that allow bee dispersal. Some hybrid fruits displayed the characteristic hollowness, resin production and resin chemistry associated with seed dispersal by bees. However, we did not observe bees foraging on any hybrid fruits until they had been damaged. We conclude that C. torelliana and C. citriodora subsp. citriodora hybrids can inherit some fruit characters that are associated with dispersal by bees, but we did not find a hybrid with the complete set of characters that would enable bee dispersal. However, around 20,000 hybrids have been planted in Australia, and ongoing monitoring is necessary to identify any hybrids that may become invasive.
Resin, a sticky sap emitting terpenoids and other volatiles, is produced by various plant species to seal wounds and protect themselves against herbivores and microbes. Among several other insects, bees have evolved the surprising ability to handle the repellent plant sap and use it to construct and defend their nests. Whereas the collection of pollen and nectar has been intensively studied in bees, resin collection has received only little attention. The aim of this dissertation was to better understand how the physiological and chemical properties of resin and resin-derived compounds (terpenes) affect the ecology of stingless bees. I therefore asked why, where and how stingless bees of Borneo (seven study-species), Australia (eight) and Costa Rica (27) collect and process plant resins, addressing the importance of a largely neglected resource not only for building and defensive properties, but also for the bees’ chemical diversity. Stingless bees are highly opportunistic resin foragers with all species collecting resin from a similar set of tree species. They locate and/or recognize resin sources on the basis of several volatile mono- and sesquiterpenes. I found that different bee species and even colonies significantly varied in the amount of resin collected. Predator attack (e.g., by ants) had the strongest affect on resin intake, whereas manual nest destruction only slightly increased the number of resin foragers. Resin is used to build, maintain and defend nests, but also as source for chemical compounds (terpenes) which stingless bees include in their surface profiles (chemical profiles). They directly transfer resin-derived compounds to their body surfaces (cuticular terpenes), but only include a subset (8 %) of the large number (>> 1000) of terpenes found in tree resins. This phenomenon can only be explained by a hitherto unknown ability to filter environmentally derived compounds which results in species-specific terpene profiles and thus in an increased chemical heterogeneity among species. Moreover, due to the addition of resin-derived substances the diversity of compounds on the bees’ body surfaces by far exceeds the chemical diversity of profiles in other hymenopterans. Because stingless bees filter but do not modify resin-derived compounds, species from Borneo, Australia and Costa Rica all resemble the characteristic resin of typical trees in their regions of origin. This chemical similarity reveals a strong correlation between the diversity of tree resins and the diversity of cuticular terpenes among stingless bees in a given habitat. Because different tree species are found in different tropical regions, the chemical composition of tree resins varies between tropical regions as does the composition of cuticular terpenes in bee species from these regions. Cuticular terpenes are however most common among stingless from Borneo, with 100 % of species studied having resin-derived terpenes in their chemical profiles. They are least common in Costa Rica, with only 40 % of species having terpenes. Likewise, resin collection was found to be highest in Tetragonilla collina colonies of Borneo where occasionally up to 90 % of foragers collected resin. By contrast, resin collection was only performed by 10 % of foragers of a given colony in Australia and by a maximum of 40 % in Costa Rica. The dominance of resin and resin-derived compounds in the chemical ecology of bees from Borneo may mirror the dominance of a particular Southeast Asian tree family: the highly resinous dipterocarps. Such a correlation between the chemistry of bees and the chemistry of tree resins therefore underlines the close relationship between stingless bees and the trees of their habitat. Cuticular terpenes are assumed to protect bees against predators and/or microbes. Sesquiterpenes, a specific group of terpenes, most vary between species and impair inter-specific aggression by reducing aggressive behavior in species without sesquiterpenes, thereby providing a novel mechanism to achieve interspecific tolerance among insects. Reduced interspecific aggression may also be an important factor enabling the non-aggressive aggregation of nests from stingless bee colonies of up to four different species, because such aggregations frequently comprise both species with and species without sesquiterpenes. Given its various functions, resin represents a highly important resource for stingless bees which directly affects their chemical ecology, defensive properties and inter-specific communication. It remains to be investigated how the bees influence the resin-derived terpene profiles on their body surface and in their nests, particularly how they manage to exclude entire groups of terpenes. Whether bees actually need a high diversity of different resin sources and therefore tree species to maintain the homeostasis of their colonies or whether they would do equally well with a limited amount of resin sources available, should also be addressed in future studies. Answers to this question will directly impair bee and forest management in (sub)tropical regions.
Honeybees (Apis mellifera) are threatened by numerous pathogens and parasites. To prevent infections they apply cooperative behavioral defenses, such as allo-grooming and hygiene, or they use antimicrobial plant resin. Resin is a chemically complex and highly variable mixture of many bioactive compounds. Bees collect the sticky material from different plant species and use it for nest construction and protection. Despite its importance for colony health, comparatively little is known about the precise origins and variability in resin spectra collected by honeybees. To identify the botanical resin sources of A. mellifera in Western Europe we chemically compared resin loads of individual foragers and tree resins. We further examined the resin intake of 25 colonies from five different apiaries to assess the effect of location on variation in the spectra of collected resin. Across all colonies and apiaries, seven distinct resin types were categorized according to their color and chemical composition. Matches between bee-collected resin and tree resin indicated that bees used poplar (Populus balsamifera, P. x canadensis), birch (Betula alba), horse chestnut (Aesculus hippocastanum) and coniferous trees (either Picea abies or Pinus sylvestris) as resin sources. Our data reveal that honeybees collect a comparatively broad and variable spectrum of resin sources, thus assuring protection against a variety of antagonists sensitive to different resins and/or compounds. We further unravel distinct preferences for specific resins and resin chemotypes, indicating that honeybees selectively search for bioactive resin compounds.
Biodiversity loss, as often found in intensively managed agricultural landscapes, correlates with reduced ecosystem functioning, for example, pollination by insects, and with altered plant composition, diversity, and abundance. But how does this change in floral resource diversity and composition relate to occurrence and resource use patterns of trap-nesting solitary bees? To better understand the impact of land-use intensification on communities of trap-nesting solitary bees in managed grasslands, we investigated their pollen foraging, reproductive fitness, and the nutritional quality of larval food along a land-use intensity gradient in Germany. We found bee species diversity to decrease with increasing land-use intensity irrespective of region-specific community compositions and interaction networks. Land use also strongly affected the diversity and composition of pollen collected by bees. Lack of suitable pollen sources likely explains the absence of several bee species at sites of high land-use intensity. The only species present throughout, Osmia bicornis (red mason bee), foraged on largely different pollen sources across sites. In doing so, it maintained a relatively stable, albeit variable nutritional quality of larval diets (i.e., protein to lipid (P:L) ratio). The observed changes in bee–plant pollen interaction patterns indicate that only the flexible generalists, such as O. bicornis, may be able to compensate the strong alterations in floral resource landscapes and to obtain food of sufficient quality through readily shifting to alternative plant sources. In contrast, other, less flexible, bee species disappear.