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.
Citation: Wallace HM, Leonhardt SD (2015) Do Hybrid Trees Inherit Invasive Characteristics? Fruits of Corymbia torelliana X C. citriodora Hybrids and Potential for Seed Dispersal by Bees. PLoS ONE 10(9): e0138868. doi:10.1371/journal.pone.0138868
Editor: Sergio R. Roiloa, University of A Coruña, SPAIN
Received: October 14, 2014; Accepted: September 4, 2015; Published: September 29, 2015
Copyright: © 2015 Wallace, Leonhardt. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited
Data Availability: All data files used for figures and tables are available from http://dx.doi.org/10.4227/39/55b994aa01438.
Funding: This work was funded in part by an Australian Research Council Linkage Grant LP0218877 to HMW and the Queensland Government Smart State Program via the Smart Forests Alliance Queensland to HMW. Funding for SDL was provided by the Deutsche Forschungs-Gemeinschaft (DFG project: LE 2750/1-1) and by a grant of the German Excellence Initiative to the Graduate School of Life Science, University of Würzburg. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors have declared that no competing interests exist.
Global interest in invasive trees is increasing and invasive trees have recently been recognized as having substantial impacts on biodiversity and ecosystem functioning . There are many factors that may contribute to trees becoming invasive, and some critical factors include tree dispersal mechanisms, hybridisation and escape from plantations. Tree species dispersed by animals are disproportionality more likely to become invasive and long-distance seed dispersal, often a feature of animal dispersal, can play a crucial role in invasions [2, 3]. Invasion may also be facilitated by hybridisation . Hybridisation is an important evolutionary process for plants that allows them to evolve rapidly and can confer new characteristics that enable plants to proliferate, persist and invade . Hybridisation between domesticated plants and wild relatives is well documented as a source of new weeds [4, 6]. Lastly, tree invasions are often driven by tree species escaping from cultivation or plantations . Thus management strategies for tree plantations need to account for the possibility of seed dispersal into surrounding areas and subsequent invasions .
Corymbia torelliana is an invasive tree species with an unusual animal dispersal mechanism [8, 9]. The tree is dispersed by stingless bees foraging for resin inside the fruit [8–11]. Stingless bees collect plant resins for nest building and defence [12, 13]. Seeds taken up by resin collecting bees may be dispersed long distances (over 300 m), and the tree is invasive in areas outside of its natural range where it co-occurs with stingless bees [8, 10]. C. torelliana is the only Corymbia species to be dispersed by bees and to be invasive. Other members of the genus are not invasive and are dispersed very short distances through barochory. Furthermore C. torelliana is invasive only in areas where it co-occurs with stingless bees [8, 10]. This suggests that this unique dispersal mechanism contributes greatly to making C. torelliana invasive. Moreover, C. torelliana (section Cadagaria) hybridizes readily with three closely related species in the spotted gum group, (section Politaria) Corymbia citriodora subsp. citriodora, C. citriodora subsp. variegata, C. henryi and C. maculata [14–17]. In addition, C. torelliana is able to form hybrids with more distantly related Corymbia species . Corymbia species and their hybrids are of increasing interest for forestry plantations globally due to their fast growth and resistance to disease. Over 20,000 ha of plantations have been established across Australia since the late 1990s primarily using Corymbia citriodora subsp. variegata [18, 19]. The C. torelliana hybrids may pose a risk to native forests if they have the same fruit characteristics that would enable long distance dispersal by bees and could allow the plantation trees to become an invasive weed . Hybrids with C. torelliana could inherit characteristics that allow them to be dispersed by bees and become invasive. However, C. torelliana has a fruit structure that is unique in Corymbia and enables seed dispersal by bees. The central column collapses and the valves retract resulting in a completely hollow fruit [20, 21]. As a result, the open fruits of C. torelliana are hollow spherical structures, which permit entry of the bees [8, 10]. To our best knowledge, the hybrid fruits have as yet not been examined to determine their structure and their attractiveness to bees.
The chemical composition of the fruit resin further plays a critical role in the relationship with the seed-dispersing bees, as bees use a complex set of olfactory cues to find the resin . Stingless bees incorporate resin compounds into their cuticle and compounds also found in C. torelliana fruit resin have been discovered in seven species of Australian stingless bees [23–25]. Bees with resin-derived compounds (including those of C. torelliana) are better protected against predators, e.g. ants  Moreover, C. torelliana resin is more effective as an antimicrobial agent than three other tree resins frequently collected by stingless bees , suggesting an important role of this resin in protecting stingless bee colonies against pathogenic microbes. Therefore, bees may even benefit from a spread of invasive C. torelliana trees. However, some beekeepers claim that C. torelliana resin may harm stingless bee colonies e.g. by causing colonies to collapse  although no evidence of this has been found in areas where they co-occur . Whether the chemical composition of resin and subsequently the chemical ecology of stingless bees collecting resin is affected by hybridisation is unknown.
The aim of this study was to investigate whether hybrids of C. torelliana have the same characteristics of the parent tree that would enable seed dispersal by bees, and may facilitate invasion. We specifically addressed the following questions: (1) what are the external and internal dimensions of hybrid fruits compared with C. torelliana (2) how frequently do hybrids display the critical characteristics of resin presented in the fruit and central column collapse associated with the C. torelliana seed dispersal syndrome (3) what hybrid fruits if any are attractive to bees? (4) what is the chemical profile of the resin from fruits of hybrids compared with C. torelliana? We expected to find some hybrids with similarities to C. torelliana that may enable long distance dispersal by bees and thus may facilitate invasion by hybrids.
Materials and Methods
We examined a windbreak planting of C. torelliana, C. citriodora subsp. citriodora and spontaneous hybrids of C. torelliana and C. citriodora subsp. citriodora on private land near Walkamin, North Qld, Australia (17° 8' 5" S, 145° 25' 41" E) (Fig 1). The owner of the land gave permission to conduct the study on this site. Corymbia species form hybrids across taxonomic groups and wide crosses between species from subgenera Blakella and Corymbia are known from natural populations  and controlled pollination studies [14, 16]. There were 97 trees of C. torelliana, C. citriodora and hybrids at the site. The parent species have very different tree form, bark and leaf characteristics. C. citriodora subsp. citriodora has pale whitish, pink or grey bark, with narrow lanceolate to lanceolate leaves with a distinctly lemon odour from the aldehyde citronellal contained in the leaves . In contrast C. torelliana is distinctly different from all other known Corymbia species, with a tessellated stocking on the lower trunk and grey green to whitish green bark above shedding in thin sheets. The juvenile leaves of C. torelliana are peltate and setose and adult leaves are often poorly developed on mature C. torelliana trees . The occurrence of C. torelliana hybrids with C. citriodora subsp. citriodora and other spotted gums and their morphological features have been widely reported in the literature [14–17]. Hybrids may have intermediate tree form, bark characteristics and leaf shapes or may show unusual combinations of parent features. Hybrids are often strikingly different from the parent species in windbreak plantings when planted alongside the parent species. We assessed morphological characteristics such as tree form, bark colour and texture, leaf shape and smell as described in  to determine the identity of all trees at the site as either pure species or hybrids. We examined all trees to determine whether they had fruits, and if so whether they were mature.
Where fruits were mature, we assessed fruit dimensions of C. torelliana, C. citriodora subsp. citriodora and hybrids of the two species. We observed 12 trees of C. torelliana, 10 trees of C. citriodora subsp. citriodora and 37 hybrid trees with mature fruits at the site during the study. We measured the fruit dimensions of 10 capsules per tree in terms of external length, external width, external rim diameter and internal rim diameter.
We examined the structure of hybrid fruits to determine whether they had the C. torelliana characteristics that may influence seed dispersal by bees. We sectioned five fruits from each of 16 hybrid trees (80 hybrid fruits) transversely and determined whether resin was present, and whether the central column had collapsed. Fruits were assigned a score of 1, 2 or 3 where 1 was little resin, 2 was some resin and 3 was copious resin. Column collapse was assigned a rank of 1, 2 or 3 where 1 was column intact, 2 was column partially collapsed and 3 was column fully collapsed. Five fruits of each of 3 C. torelliana and C. citriodora subsp. citriodora were sectioned to assist in comparing the hybrids with the parent species.
C. torelliana, C. citriodora subsp. citriodora and hybrids were examined for 10 days over 3 fruiting seasons between 2002 and 2005 to determine whether bees foraged for resin on the fruits and whether bees subsequently dispersed seeds. All observations were carried out between 09.30 and 0.4.30 during sunny weather conducive to bee activity. Each tree was initially examined to determine the maturity of the fruits. Corymbia species typically have clusters of fruits that protrude from the canopy of the tree .
The fruit clusters with up to 50 fruits were examined for signs of opening, e.g. mottled green/brown in colour and opening valves. Where fruits were opening, they were observed for 5 minutes for bee activity using Zeiss 8 X 30 binoculars. For each tree observed, the number of bees foraging on the cluster of fruit during the 5 minute observation period was recorded. Fruits were observed to determine whether bees landed on the outside and entered the fruits. If bees were observed leaving the fruits, observations were made on whether they carried resin, chaff or seeds. One cluster of fruits per tree was observed for 5 minutes for each tree for each day. Observations on all trees were repeated every 2–4 days over 2–3 weeks in 2004 and 2005. In preliminary observations, we found that bees foraged on hybrid fruits that had been chewed and discarded by red tailed black cockatoos. Where trees had fruits that had been discarded on the ground, we conducted further observations of bee activity on the ground for a 5 minute period. We observed all fruits on the ground within a 3m× 3m square to determine whether bees were attracted to fruits.
To test whether the chemical composition of resin in fruits of C. torelliana×C. citriodora hybrids and C. torelliana differed qualitatively (presence/absence of compounds) and/or quantitatively (different proportions of compounds), resin was analysed using gas chromatography (GC) and mass spectrometry (MS) as described in . GC separates compounds according to their molecular weight and chemical structure, and MS breaks them down into fragments that are typical for specific compounds (classes). These fragments can then be used for identification and comparison with references.
We analysed resin from three C. torelliana and three hybrid trees. Resin of C. torelliana has previously been analysed and shows little variation between trees or populations (see  ), which is why we considered three trees sufficient as a reference to which we could compare resin from hybrids. However, although we obtained capsules from overall 16 hybrids, only three of them produced fruits with sufficient amounts of resin for chemical analyses. Where available, resin of 3–5 fruits (between 5–30 μl resin/ fruit) per tree was extracted with a clean knife and forceps and transferred to 2.5 ml glass vials containing hexane (p.a. grade, Sigma-Aldrich, Munich, Germany).
For characterization of compounds we used a Hewlett Packard HP 6890 Series GC System coupled to a Hewlett Packard HP 5973 Mass Selective Detector (Agilent Technologies, Böblingen, Germany). The GC was equipped with a J & W, DB-5 fused silica capillary column (30m x 0.25 mm ID; df = 0.25 μm; J & W, Folsom, CA, USA). Temperature was programmed from 60°C to 300°C with 5°C/min heating rate and held for 10 min at 300°C. We used helium as carrier gas (constant flow of 1 ml/min). Injection was carried out at 250°C in the splitless mode for 1 min. The electron impact mass spectra (EI-MS) were recorded at 70 eV and 230°C. Windows version of the ChemStation software package (Agilent Technologies, Böblingen, Germany) was used for data acquisition and analysis.
Chemical compounds found in hexane extracts of resin were characterized by their mass spectra and their retention times. We regarded peaks with identical mass spectra and retention times as the same compound. Three commercially available mass spectra libraries (Wiley 275, NIST 98 and Adams EO library 2205) were used to determine compound classes with regard to their mass spectra and retention indices (Kovats Index). Moreover, all alkanes were confirmed by synthetic standards (Sigma-Aldrich, Munich, Germany). Aldehydes, alcohols and esters as well as terpenes were tentatively identified by comparison of the obtained mass spectra with mass spectra and retention indices in libraries. Comparisons with synthetic standards (Sigma-Aldrich, Munich, Germany) were performed if standards were available. Data of terpenes were further compared with those of dipterocarp and pine tree resins that typically comprise di-, sesqui- and triterpenes .
All data on fruit dimensions were analysed with a nested ANOVA with taxa and tree (nested within taxa) as factors followed by Tukey’s HSD test where significant differences between taxa were detected. Prior to the statistical analysis of chemical compounds, trace compounds for which mass spectra could not be interpreted as well as compounds which accounted for less than 0.5% of the total peak area in all samples were removed from the dataset (if a compound accounted for more than 0.5% in one samples, it was included in the analysis although it may have accounted for less than 0.5% in other samples). The analysis was based on a total of 97 compounds. These compounds were quantified as proportions by dividing the peak area of each compound by the total area of all sample peaks included in the analysis.
We examined the chemical variation among resins from C. torelliana and hybrid trees using (a) all compounds, and (b) only volatile compounds. We considered compounds volatile when they eluted from the GC column prior to 23 min sample run time. In doing so, we may have included few non-volatile polar compounds, but the dataset will be largely confined to volatile compounds. We then analysed chemical variation between tree resins by a multivariate matrix permutation test based on the Bray-Curtis distances between compounds using the ADONIS function in the VEGAN package in R. To identify compounds contributing to the variation observed between resins of C. torelliana and hybrids, a principal covariate analysis (PCoA) also based on Bray-Curtis distances was performed. Finally, a hierarchical cluster analysis based on the Bray-Curtis distances between compounds was used to produce figures. All statistical analyses were performed in R .
Fruit dimensions and characteristics
There were significant differences between the three taxa in all fruit dimensions sampled. Both C. torelliana and C. citriodora subsp. citriodora were significantly shorter than hybrids (F = 165.23, P<0.0001, Fig 2A). C. torelliana was significantly wider than C. citriodora subsp. citriodora with hybrids showing intermediate width (F = 383.64, P<0.0001, Fig 2B). Hybrids had a significantly larger external rim than both species (F = 81.59, P<0.0001, Fig 2C). The internal rim was widest for C. torelliana, smallest for C. citriodora subsp. citriodora and hybrids were intermediate (F = 272.46, P<0.0001, Fig 2D). Within the three taxa there were significant differences between individual trees for height, width, external rim and internal rim (F = 27.27, F = 32.16, F = 24.44, F = 21.49 respectively, P<0.0001 in all cases).
Means and standard errors are presented, means with different letters are significantly different (Tukey’s HSD, P<0.05)
All fruits had resin present, although 6 of the 16 hybrid fruits sectioned had very little (characteristic of C. citriodora, Table 1, Fig 3B). Only one hybrid displayed the copious and viscous resin characteristic of C. torelliana (Fig 3A). Similarly, only four of the 16 hybrids examined showed complete central column collapse, characteristic of C. torelliana, and 5 showed intermediate column collapse (Figs 3C and 2D; Table 1). Seeds in some hybrid capsules were noticeably larger than C. torelliana (Fig 3C).
All bars = 2mm A. C. torelliana fruit showing hollow structure with copious resin (black arrows). Note the width of the internal rim (r) B. C. citriodora subsp. citriodora showing central column (cc) and small internal dimensions and small woody rim (r). C. C. torelliana ×C. citriodora subsp. citriodora hybrids partial central column (cc) and large seed (s) Note the small rim (r) compared with A, and the presence of small amounts of resin (black arrow). D. C. torelliana ×C. citriodora subsp. citriodora hybrid showing partial central column (cc). note the large rim (r).
Bees did not visit fruits on trees of any hybrids or of C. citriodora subsp. citriodora. In contrast, at the same site, there were on average 2.75 bee visits per 5 minutes to the C. torelliana fruits (Table 2). Bees visiting the C. torelliana fruits were frequently observed entering capsules and carrying resin loads in their corbiculae when leaving capsules. Bees frequently visited broken fruits of hybrids on the ground to collect resin from the wound tissue (Table 2). Bees were observed carrying resin and chaff from these fruits, but seed dispersal by stingless bees from these fruits was not observed.
Resins of three C. torelliana trees and three hybrids differed significantly in their chemical composition (Adonis, all compounds: R2 = 0.43, P < 0.001, Fig 4), as resins of hybrid 85 and hybrid 87 were chemically more distant from C. torelliana resin than resin of hybrid 89 (Fig 4). Differences were both qualitative and quantitative and could be attributed to several mono- and sesquiterpenes as well as to several unidentified non-volatile compounds (Table 3). However, when only volatile compounds were considered, resins from C. torelliana and hybrids did not significantly differ in their chemical composition (Adonis: R2 = 0.35, p = 0.10).
Ranges where monoterpenes (MT), sesquiterpenes (ST) and non-volatile compounds, such as triterpenes (TT), typically dilute in our method are indicated by brackets. Arrows mark a flavonoid (C15H22O3) characteristically found in resin of C. torelliana fruits.
Hybridisation between plants may result in novel genotypes, and/or may increase genetic variation, and/or may result in fixed heterosis thus giving hybrids adaptive advantages that enable them to become invasive . Our study shows that hybrids can inherit some of the characteristics of C. torelliana that theoretically enable them to be dispersed by bees. Some fruits inherited characteristics such as column collapse, copious quantities of resin and similar fruit dimensions to C. torelliana. Resin chemistry in one out of three hybrids examined was also quite similar to C. torelliana. However, due to the large variation in resin chemistry between hybrids and the limited sample size of only three trees analysed, conclusions with regard to resin chemistry need to be confirmed by additional analyses.
Fruit features such as size, hollowness, resin production and seed size were variable in hybrids compared to C. torelliana and C. citriodora. Fruit size is a crucial characteristic of C. torelliana that enables bee dispersal as bees can only gain entry if the fruit is large enough . Hybrid fruits were on average intermediate in size between the parent species, but there was variability in the hybrids and some trees had fruits that were similar in size to C. torelliana. Those with similar fruit dimensions to C. torelliana are the most likely to allow bees to enter, and could potentially be dispersed by bees.
If bees can gain entry to the fruits they also need to be able to manoeuvre inside the fruit to collect resin [8, 10]. The C. torelliana fruit is hollow and this enables bees to manoeuvre. The hollowness is caused by the collapse of the central column and is to date has only been reported for C. torelliana. In this study four hybrids trees also showed complete column collapse, similar to C. torelliana. This indicates that this capsule characteristic is inherited by some hybrids and would facilitate bee entry into the capsule.
In other plants that are dispersed by bees, the bees collect the mucilaginous sticky exocarp and seeds , or collect resin and seeds from the exposed pod . C. torelliana presents copious quantities of resin inside the fruits and this is a crucial adaptation to seed dispersal by stingless bees, because it attracts the bees and allows the seeds to attach to the bees’ corbiculae . All hybrid fruits contained some resin, and one hybrid even showed similar resin quantities to C. torelliana. Interestingly bees foraged on hybrid fruits only when they had been damaged by cockatoos and the resin had been exposed, suggesting that bees were not able to access the hybrid resins in the fruits when they were intact. Clearly the resin is attractive to the bees, but the hybrid fruit structure may have prevented bees from detecting the resin and thus foraging on it.
Seed size of hybrids was noticeably larger than C. torelliana in some hybrids (Fig 3C). Bees can transport up to 4 C. torelliana seeds at one time so the larger hybrid seeds are unlikely to prevent seed transport completely, although the larger hybrid seeds are likely to be harder to transport by bees .
C. torelliana resin can easily be distinguished from resins of other tree species. It consists of a variety of terpenoids, phloroglucinols and flavonoids, with minor differences between trunk resin and fruit resin [34, 35]. Stingless bees accurately learn its volatile profile as minor changes to the profile strongly reduce the attraction of bees . This high cue specificity shown by bees indicates that C. torelliana fruit resin chemistry is highly species-specific.
We found that one hybrid had a chemical profile that was very similar to C. torelliana, whereas the two others differed in the proportions of some compounds or were even entirely lacking compounds typically found in C. torelliana resin. Consequently, the resin of hybrids can strongly resemble C. torelliana resin, particularly with regard to volatile compounds. Because stingless bees use a blend of volatile mono- and sesquiterpenes to find resin sources and are very specific in their olfactory search ‘image’ when foraging on C. torelliana fruit resin [22, 24], they may be as strongly attracted to the hybrid resin as to C. torelliana resin, unless morphological fruit characteristics prevent them from actually smelling the resin. However, this assumption needs to be confirmed by additional analyses of hybrid resin samples.
Some hybrid fruits showed the critical features of C. torelliana fruit structure that are essential for long distance dispersal by bees. However, we did not actually observe bees foraging on intact hybrid fruits of C. torelliana in this study. Moreover, we did not find a hybrid with the complete set of characters that would enable seed dispersal. This suggests that fruit characteristics that enable bee dispersal are not inherited together and are probably under the control of many genes. Many traits of eucalypts are inherited in a more-or-less intermediate manner in F1 hybrids, although there are exceptions, and dominance or partial dominance of parental traits have sometimes been reported . For example, leaf chemistry of C. torelliana hybrids shows complex heritability patterns. Hybrids between C. torelliana and C. citriodora subsp. variegata show intermediate chemical leaf profiles, or contain compounds from both parents [37, 38]. In contrast, the foliar chemistry of hybrids between C. torelliana and C. citriodora subsp. citriodora and C. henryi was always dominated by the C. torelliana parent.
Although bee dispersal of hybrids was not observed in this study, we examined only hybrids between C. torelliana and C. citriodora subsp. citriodora. Further study on other hybrids is needed to more completely assess the risk of bee dispersal. The risk of seed dispersal by bees in hybrids will depend on how frequently, and in what combinations the C. torelliana fruit characters occur in the hybrid population. Spotted gums may inherit some of the C. torelliana fruit characteristics from hybrids as hybrids can successfully backcross onto the parents . Around 20,000 hybrids have been planted in Australia  and large scale hybridisation programs are still underway. These hybrids include species not examined in this study such as C. citriodora subsp. variegata and C. henryi. It is likely that some of these hybrids inherit the adaptive advantages such as long distance seed dispersal that enable them to become invasive . We therefore need ongoing monitoring of fruit characteristics in these hybrids to minimize the chance of long distance seed dispersal and invasion by these hybrid plantation trees.
We thank R. Stokoe for field assistance and providing the data on fruit size, and David Walton for help with figures. We are further grateful for the comments of two anonymous reviewers which greatly improved the presentation of our study.
Conceived and designed the experiments: HMW SDL. Performed the experiments: HMW SDL. Analyzed the data: HMW SDL. Contributed reagents/materials/analysis tools: HMW SDL. Wrote the paper: HMW SDL.
- 1. Richardson DM, Rejmanek M. Trees and shrubs as invasive alien species—a global review. Diversity and Distributions. 2011;17(5):788–809. doi: 10.1111/j.1472-4642.2011.00782.x pmid:WOS:000294655400002.
- 2. Lesser M, Jackson S. Contributions of long-distance dispersal to population growth in colonising Pinus ponderosa populations. Ecology Letters. 2013;16:380–9 doi: 10.1111/ele.12053. pmid:23279647
- 3. Richardson DM, Allsopp N, D'Antonio CM, Milton SJ, Rejmanek M. Plant invasions—the role of mutualisms. Biological Reviews. 2000;75(1):65–93. doi: 10.1017/s0006323199005435 pmid:WOS:000086077500003.
- 4. Schierenbeck KA, Ellstrand NC. Hybridization and the evolution of invasiveness in plants and other organisms. Biological Invasions. 2009;11(5):1093–105. doi: 10.1007/s10530-008-9388-x pmid:WOS:000265084200003.
- 5. Wu W, Zhou R-C, Ni G-Y, Shen H, Ge X-J. Is a new invasive herb emerging? Molecular confirmation and preliminary evaluation of natural hybridization between the invasive Sphagneticola trilobata (Asteraceae) and its native congener S. calendulacea in South China. Biological Invasions. 2013;15(1):75–88. doi: 10.1007/s10530-012-0269-y pmid:WOS:000312140800007.
- 6. Vigueira CC, Olsen KM, Caicedo AL. The red queen in the corn: agricultural weeds as models of rapid adaptive evolution. Heredity. 2013;110(4):303–11. doi: 10.1038/hdy.2012.104. pmid:23188175
- 7. Caplat P, Hui C, Maxwell BD, Peltzer DA. Cross-scale management strategies for optimal control of trees invading from source plantations. Biological Invasions. 2014;16(3):677–90. doi: 10.1007/s10530-013-0608-7 pmid:WOS:000330774900014.
- 8. Wallace HM, Howell MG, Lee DJ. Standard yet unusual mechanisms of long-distance dispersal: seed dispersal of Corymbia torelliana by bees. Divers Distrib. 2008;14(1):87–94. pmid:ISI:000251584500010.
- 9. Wallace HM, Lee DJ. Resin-foraging by colonies of Trigona sapiens and T. hockingsi (Hymenoptera: Apidae, Meliponini) and consequent seed dispersal of Corymbia torelliana (Myrtaceae). Apidologie. 2010;41(4):428–35. doi: 10.1051/apido/2009074 pmid:WOS:000280290600002.
- 10. Wallace HM, Trueman SJ. Dispersal of Eucalyptus torelliana seeds by the resin-collecting stingless bee, Trigona carbonaria. Oecologia. 1995;104(1):12–6. pmid:ISI:A1995RZ35900002.
- 11. Leonhardt SD, Heard TA, Wallace H. Differences in the resource intake of two sympatric Australian stingless bee species. Apidologie. 2014;45(4):514–27. doi: 10.1007/s13592-013-0266-x pmid:WOS:000338216700012.
- 12. Leonhardt S, Blüthgen N. A sticky affair: resin collection by Bornean stingless bees. Biotropica 2009;41:730–6.
- 13. Roubik DW. Stingless bee nesting biology. Apidologie. 2006;37(2):124–43. pmid:ISI:000238477400002.
- 14. Dickinson GR, Wallace HM, Lee DJ. Controlled pollination methods for creating Corymbia hybrids. Silvae Genetica. 2010;59(5):233–41. pmid:WOS:000287178600005.
- 15. Dickinson GR, Lee DJ, Wallace HM. The influence of pre- and post-zygotic barriers on interspecific Corymbia hybridization. Annals of Botany. 2012;109(7):1215–26. doi: 10.1093/aob/mcs050 pmid:WOS:000304532300002.
- 16. Dickinson GR, Wallace HM, Lee DJ. Reciprocal and advanced generation hybrids between Corymbia citriodora and C. torelliana: forestry breeding and the risk of gene flow. Annals of Forest Science. 2013;70(1):1–10. doi: 10.1007/s13595-012-0231-2 pmid:WOS:000312770700001.
- 17. Hill KD, Johnson LAS. Systematic studies in the eucalypts 7. A revision of the bloodwoods, genus Corymbia (Myrtaceae). Telopea. 1995;6:185–504.
- 18. Barbour RC, Crawford AC, Henson M, Lee DJ, Potts BM, Shepherd M. The risk of pollen-mediated gene flow from exotic Corymbia plantations into native Corymbia populations in Australia. Forest Ecology and Management. 2008;256(1–2):1–19. doi: 10.1016/j.foreco.2008.03.028 pmid:ISI:000257625100001.
- 19. Lee D. Development of Corymbia species and hybrids for plantations in eastern Australia. Australian Forestry 2007;70:11–7.
- 20. Boland D. Dehiscence in Eucalyptus torelliana F.Muell. fruit. Australian Seed Science Newsletter 1976;2:11–3.
- 21. Carr D, Carr S. Eucalyptus II. The rubber cuticle, and other studies of the Corumbosae. Canberra, Australia: Phytoglyph Press; 1987.
- 22. Leonhardt S, Baumann A, Wallace H, Brooks P, Schmitt T. The chemistry of an unusual seed dispersal mutualisim: bees use a complex set of olfactory cues to find their partner. Animal Behaviour 2014;in press.
- 23. Leonhardt SD, Blüthgen N, Schmitt T. Smelling like resin: terpenoids account for species-specific cuticular profiles in Southeast-Asian stingless bees. Insect Soc. 2009;56:157–70. doi: 10.1007/s00040-009-0007-3.
- 24. Leonhardt SD, Wallace HM, Schmitt T. The cuticular profiles of Australian stingless bees are shaped by resin of the eucalypt tree Corymbia torelliana. Austral Ecology. 2011;36(5):537–43. doi: 10.1111/j.1442-9993.2010.02184.x pmid:WOS:000293065900013.
- 25. Leonhardt SD, Schmitt T, Blüthgen N. Tree resin composition, collection behavior and selective filters shape chemical profiles of tropical bees (Apidae: Meliponini). Plos One. 2011;6(8):e23445. doi: 10.1371/journal.pone.0023445 pmid:WOS:000293773300030.
- 26. Leonhardt SD, Wallace HM, Blüthgen N, Wenzel F. Potential role of environmentally derived cuticular compounds in stingless bees. Chemoecology. 2015. doi: 10.1007/s00049-015-0185-6.
- 27. Drescher N WH, Katouli M, Massaro C, Leonhardt SD Diversity matters: how bees benefit from different resin sources. Oecologia 2014; doi: 10.1007/s00442-014-3070-z. pmid:25205030
- 28. Klumpp J. Australian stingless bees-a guide to sugarbag beekeeping. West End, Australia: Earthling Enterprises; 2007. 120 p.
- 29. Massaro FC, Brooks PR, Wallace HM, Russell FD. Cerumen of Australian stingless bees (Tetragonula carbonaria): gas chromatography-mass spectrometry fingerprints and potential anti-inflammatory properties. Naturwissenschaften. 2011;98(4):329–37. doi: 10.1007/s00114-011-0770-7 pmid:WOS:000289258400006.
- 30. Langenheim JH. Plant resins: chemistry, evolution, ecology and ethnobotany. Portland, Oregon: Timber Press; 2003. 586 p.
- 31. R-Development-Core-Team. R: A language and environment for statistical computing, ISBN 3-900051-07-0. Available: http://www.R-project.org. Vienna, Austria: R Foundation for Statistical Computing; 2009.
- 32. Nunez CV, de Oliveira ML, Lima RD, Diaz IEC, Sargentini E, Pereira OL, et al. Chemical analyses confirm a rare case of seed dispersal by bees. Apidologie. 2008;39(6):618–26. doi: 10.1051/apido:2008047 pmid:ISI:000261936100002.
- 33. Bacelar-Lima C, Freire D, Coletto-Silva A, Costa K, Laray J, Vilas-Boas H, et al. Melitocory of Zygia racemosa (Ducke) Barneby & Grimes by Melipona seminigra merrillae Cockerell, 1919, and Melipona compressipes manaosensis Schwarz, 1932 (Hymenoptera, Meliponina) in Central Amazon, Brazil. Acta Amazon 2006;36:343–8.
- 34. Massaro CF, Smyth TJ, Smyth WF, Heard T, Leonhardt SD, Katouli M, et al. Phloroglucinols from anti-microbial deposit-resins of Australian stingless bees (Tetragonula carbonaria). Phytotherapy Research. 2015;29(1):48–58. doi: 10.1002/ptr.5225. pmid:25230727
- 35. Nobakht M, Grkovic T, Trueman SJ, Wallace HM, Katouli M, Quinn RJ, et al. Chemical constituents of kino extract from Corymbia torelliana. Molecules. 2014;19(11):17862–71. doi: 10.3390/molecules191117862. pmid:25375331
- 36. Potts BM, Dungey HS. Interspecific hybridization of Eucalyptus: key issues for breeders and geneticists. New Forests. 2004;27(2):115–38. pmid:ISI:000184691000002.
- 37. Nahrung HF, Waugh R, Hayes RA. Corymbia species and hybrids: chemical and physical foliar attributes and implications for herbivory. Journal of Chemical Ecology. 2009;35(9):1043–53. doi: 10.1007/s10886-009-9682-9 pmid:WOS:000270634300005.
- 38. Hayes RA, Nahrung HF, Lee DJ. Consequences of Corymbia (Myrtaceae) hybridisation on leaf-oil profiles. Australian Journal of Botany. 2013;61(1):52–9. doi: 10.1071/bt12224 pmid:WOS:000315153600006.