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Acta Botanica Brasilica

Print version ISSN 0102-3306On-line version ISSN 1677-941X

Acta Bot. Bras., ahead of print  Epub July 02, 2018

http://dx.doi.org/10.1590/0102-33062018abb0143 

Article

Are native bees and Apis mellifera equally efficient pollinators of the rupestrian grassland daisy Aspilia jolyana (Asteraceae)?

Pietro K. Maruyama1  2  * 
http://orcid.org/0000-0001-5492-2324

Carlos E. P. Nunes1 
http://orcid.org/0000-0002-7534-0697

Jeferson Vizentin-Bugoni3 
http://orcid.org/0000-0002-6343-3650

Simone Gustafsson4 
http://orcid.org/0000-0001-6209-3052

Leonor Patricia Cerdeira Morellato5 
http://orcid.org/0000-0001-5265-8988

1Departamento de Biologia Vegetal, Instituto de Biologia, Universidade Estadual de Campinas, 13083-970, Campinas, SP, Brazil

2Instituto de Biologia, Universidade Federal de Uberlândia, 38405302, Uberlândia, MG, Brazil

3Natural Resources and Environmental Sciences Department, University of Illinois at Champaign-Urbana, 61820, Urbana, IL, USA

4Center for Macroecology, Evolution and Climate, Natural History Museum of Denmark, University of Copenhagen, 2100, Copenhagen, Denmark

5Laboratório de Fenologia, Departamento de Botânica, Instituto de Biociências, Universidade Estadual Paulista, 13506-900, Rio Claro, SP, Brazil

ABSTRACT

Most angiosperms rely on animals for pollination, and insects, especially bees, are being the most frequent pollinators. Many native Neotropical plants are frequently visited by the invasive honeybee (Apis mellifera), but its role in the pollination of these plants has been little investigated. We assessed the contribution of various floral visitors, including native bees and the honeybee, on the pollination of a generalist rupestrian grassland daisy, Aspilia jolyana (Asteraceae), in Serra do Cipó, Espinhaço Mountain Range, Brazil. We recorded floral visitors and measured the seed set resulting from one single visitation. We observed a total of 442 visits, mostly by bees, with Bombus pauloensis and Apis mellifera being the most common floral visitors. Other visitors included many other species of bees, flies, hummingbirds, wasps and butterflies. Pollinators significantly increased seed set in comparison to non-visited (bagged) capitula. Moreover, there was no difference among bee species/groups in their contribution to seed set. Thus, A. jolyana benefits from its generalized pollination strategy, and frequent bee visitors, including several native species and the invasive honeybee, are equally effective pollinators for this generalist daisy of rupestrian grasslands.

Keywords: bee pollination; Bombus pauloensis; generalization; honeybee; invasive species; pollination efficacy; Serra do Cipó

Introduction

Generalization in interactions with pollinators may ensure plant reproduction in face of spatio-temporal variation in the availability of floral visitors (Waser et al. 1996; Brito et al. 2017). In fact, many flowers are visited by a range of species and functional groups of animals, thus are both ecologically and functionally generalists (Ollerton et al. 2007). Such generalist species are regarded as the main contributors to the dynamics and stability of the interaction networks between plants and floral visitors/pollinators (Martín González et al. 2010). However, not all floral visitors are true pollinators and there may be considerable variation in the efficacy of different species comprising the pollinator fauna of a particular plant (e.g. Fumero-Cabán & Meléndez-Ackerman 2007). Because of this, the perceived level of generalization in plant-pollinator interaction is likely overestimated, and when the efficacy of each pollinator is taken in account, higher specialization is often reported (King et al. 2013).

To assess the importance of distinct floral visitors as pollinators for a given plant, one can experimentally control the exposition of flowers to specific visitors, and then assess their efficacy as pollinators by recording the number of pollen grains deposited on stigmas or fruit/seed set resulting from each single visit (e.g. Freitas & Paxton 1998; King et al. 2013). The inclusion of efficacy measures shows that plant-pollinator interactions exhibit some consistent trend for specialization (Rosas-Guerrero et al. 2014; but see Ollerton et al. 2015), in which pollinator functional groups are most effective pollinators to plants showing a given set of floral traits - or syndromes (Fenster et al. 2004; King et al. 2013; Rosas-Guerrero et al. 2014). Yet, it is possible that even within a functional group of pollinators, for instance bees, there are differences on pollinator efficacy related to specific life-history traits such as sociality and behavior while visiting the flowers (Westerkamp 1991).

In this context, the invasive honeybee, Apis mellifera is often regarded as an ineffective pollinator despite its overwhelming abundance (Hung et al. 2018). For instance, A. mellifera can collect nectar while avoiding contact with pollen and may even remove pollen grains from stigmas (Westerkamp 1991; Gross & Mackay 1998; Vicens & Bosch 2000). Furthermore, because of its high abundance, it can suppress the activity of native bees through exploitative competition (Dupont et al. 2004; Thomson 2004). Nevertheless, A. mellifera can still provide sufficient pollination for plants (e.g., Freitas & Paxton 1998; Fumero-Cabán & Meléndez-Ackerman 2007), and there has been a great interest in contrasting the effectiveness of the honeybee with that of other indigenous floral visitors (e.g. Freitas & Paxton 1998; Vicens & Bosch 2000; Rader et al. 2009; Hung et al. 2018). Finally, assessing the role of invasive and dominant floral visitors such as A. mellifera in plant reproduction can benefit conservation planning and management strategies (e.g. Gross & Mackay 1998).

Here, we characterize the pollinator fauna of the daisy Aspilia jolyana (Asteraceae) from the Brazilian mountain rupestrian grasslands, a megadiverse and threatened habitat (Silveira et al. 2016). Previous studies found this species to be a hub (generalist species connected to many others) in the network of plants and pollinators during the peak flowering period in rupestrian grasslands community (Carstensen et al. 2014; 2016). While recording the floral visitors, we experimentally quantified the efficacy of the most common bee visitors in facilitating pollination by quantifying the seed set, i.e., conversion of flowers to achenes, after controlled single visitation experiments (sensu Freitas 2013). We were interested in the role of different floral visitors as pollinators for this plant. Moreover, the role of the invasive honeybee in pollination is rarely assessed with experiments (Hung et al. 2018), even though A. mellifera is often a dominant floral visitor in diverse Neotropical communities (Souza et al. 2018). Thus, we asked whether invasive Apis mellifera and native bees have different effectiveness as pollinators of a generalist native plant.

Materials and methods

Study site and species

The study was conducted in October and November of 2016, in Serra do Cipó, which is located at the south of the Espinhaço Mountain Range, state of Minas Gerais, SE Brazil. We collected our data in the same locations previously sampled by Carstensen et al. (2014; 2016). The vegetation in the studied area, at ca. 1000~1200 m a.s.l., is campo rupestre or rupestrian grasslands, a species rich mountain vegetation characterized by small herbs and shrubs associated with rocky outcrops (Silveira et al. 2016; Morellato & Silveira 2018).

Asteraceae is the most species rich plant family in the rupestrian grasslands (Silveira et al. 2016; Mota et al. 2018) and the studied species, Aspilia jolyana G.M.Barroso (Asteraceae) is one of the most abundant non-grass plant species in the area, especially at elevations around 1200 m a.s.l (Mota et al. 2018). Flowers of A. jolyana form a capitulum of 10.5±1.1 mm in length and 5.6±0.7 mm in diameter (n=18 capitula), with each floret having a tube of 5.7±1.2 mm (n=20 florets from 10 capitula) and providing 1.2±0.3 μl of nectar with 27.6±6.4% of sugar concentration (n=12 florets from 7 capitula). In each capitulum, we counted 24.4±4.9 florets (n=76 capitula). The florets are protandrous, with initial pollen release by anthers. After one day, there is emergence and opening of the bifid stigma from the floral tube with elongation of the style. New stigmas emerge within the same capitulum for approximately one week.

Floral visitors and single visitation experiment

In total, we conducted 102 hours of focal plant observation in A. jolyana, from 08:00 to 16:00. We recorded all visitors, their number of visits, and we captured the insects for posterior identification whenever possible. To assess the efficacy of floral visitors as pollinators, we selectively exposed previously bagged capitula (i.e. bagged before anthesis of any floret) to distinct visitor species/groups. We refer to efficacy as the per visit effect of floral visitors in seed set, and effectiveness when combining efficacy with the visitation frequency to express the overall importance of each pollinator species/groups (sensuFreitas 2013). Before any visit, we counted the number of exposed stigmas, as indicative of female phase flowers, and after the visitation we bagged the capitulum again. We later collected the bagged capitula, after the senescence of all florets and counted the number of mature achenes (Fig. S1 in supplementary material, n=76). The proportion of female flowers (stigmas) open at the moment of visit converted into achenes was taken as the measure of pollinator efficacy. Control treatments of bagged flowers not exposed to visitors revealed that this plant is able to spontaneously self-pollinate (n=56, see Results). Hence, in some instances more achenes were formed than the number of stigmas open at the moment of the visit (in 19.7 % of the samples). We set an upper limit of 100 % for the rate of conversion to achene in such cases, as spontaneous self-pollination had in general low rate of flower to achene conversion (see Results). Our approach is based on the comparison of the relative contribution of different visitors, as there is no a priori reason to believe that self-pollination rates are different among distinct floral visitors. We reasoned that our response variable indicates the increment in seed set per capitulum when there is visitation, in contrast to spontaneous seed set. We also marked flowers exposed to free visitation and counted the total number of exposed stigmas in the capitulum and later the number of achenes as controls (n=91) besides the permanently bagged flowers.

Data analysis

First, we compared the proportion of female flowers converted into achenes between the capitula from three different categories: (1) open visitation; (2) isolated from visitors and (3) all the single visitation flowers. To do so, we ran a Generalized Linear Model (GLM) with binomial distribution for proportion data, with seed set as the response variable and the exposition category as the predictor (Zuur et al. 2009). After detecting overdispersion, we re-ran the analysis assuming a quasi-binomial distribution (Zuur et al. 2009). Model residuals were checked for model validation. After finding a significant difference among categories, we ran a post-hoc Tukey test.

Second, we compared the specific efficacy among three species and two functional groups of the most frequent bee pollinators: Bombus pauloensis, Apis mellifera, small bees, Megachilidae bees and Melipona quinquefasciata. Together these bees performed 87.8 % of the total visits and 89.5 % of the single visitation trials (see Tab. 1). For this, we ran a second GLM with binomial distribution, with seed set as response variable and the bee pollinator as predictor (Zuur et al. 2009). We checked for overdispersion and distribution of the residuals to validate the model (Zuur et al. 2009). All analyses were conducted in R (R Core Team 2016).

Table 1  List and functional group of floral visitors recorded in Aspilia jolyana (Asteraceae) at the Serra do Cipó, Brazil. The number of capitula samples for single visitation experiment is also shown. For the comparison among bee groups (Fig. 2B), small bees (marked with *) and Megachilidade bees (marked with †) were grouped together. 

Fuctional groups / Floral visitors Number of visits Single visitation samples
Beesbold>
Bombus pauloensis 190 17
Apis mellifera 106 21
Megachile sp.† 31 5
Dialictus sp.* 21 8
Melipona quinquefasciata 11 4
Pseudagapostemon ochromerus* 8 3
Augochloropsis sp.1* 7 5
Ceratina sp.* 6 2
Dichranthidium sp.1† 6 2
Tetrapedia sp. 6
Megachile iheringi 4
Trigona spinipes 3
Augochloropsis sp.2* 2 1
Centris tarsata 2
Centris sp. 1
Centris spilopoda 1
Megachilidae sp. 1
Fliesbold>
Toxomerus sp. 7 3
Syrphidae sp.1 1
Syrphidae sp.2 1
Muscidae sp. 1 1
Hummingbirdsbold>
Heliactin bilophus 3
Chlorostilbon lucidus 1
Colibri serrirostris 1 1
Waspsbold>
Braconidae sp.1 2 1
Braconidae sp.2 1 1
Scoila sp1. 1
Scoila sp2. 6
Othersbold>
Hymenoptera sp. 1 1
Lepidoptera sp.1 1
Lepidoptera sp.2 9

Results

In total, we recorded 442 visits by 31 species (or morphospecies) of floral visitors in A. jolyana. Bees were more frequent visitors than other groups (Tab. 1; Fig. 1). Nevertheless, butterflies, flies, wasps and hummingbirds were recorded visiting the flowers legitimately. Exposition to floral visitors significantly affected seed set ( 2 = 49.5, P < 0.001; post hoc Tukey test between all categories P < 0.01; Fig. 2A). Seed set was higher in open capitula (24.4±8.5 % of florets turned into achene per capitulum) than in bagged capitula (12.1±9.3 %), with capitula exposed to only one visit setting an intermediary number of seeds (17.6±12.0 %). When comparing the most frequent bee pollinators, however, no significant difference on pollination efficacy was observed between native bees or in relation to invasive Apis melifera ( 2 = 1.9, P = 0.75; Fig. 2B).

Figure 1  Some of the most frequent bee pollinators of Aspilia jolyana. A. Bombus pauloensis; B. Apis mellifera; C. Pseudoagapostemon ochromerus; D. Melipona quinquefasciata. Photos by J. Vizentin-Bugoni. 

Figure 2  Seed set (conversion of florets to achenes) in Aspilia jolyana. A. Comparison of open visitation control (unrestricted visitation), no visits control (bagged) and single visitation capitula. Different letters denote statistically significant differences between categories (GLM, ꭓ2 = 49.5, P < 0.001; post hoc Tukey P < 0.01). B. Comparison of pollination efficiency among the different bee species and groups showed no difference (ꭓ2 = 1.9, P = 0.75). See Table 1 for detail on the grouping of different bee species/morphospecies (small bees * and Megachilidade bees †). 

Discussion

Aspilia jolyana is indeed a generalist plant species, as indicated by a previous study that recorded 117 visits by 30 pollinator species to this plant in 252 hours of community-wide observations (Carstensen et al. 2014). Notably, our species-specific study only slightly increased the richness of pollinators to 31 species, performing 442 visits. However, only a conservative estimate of 29.0% species/morphospecies (n=9) found here were also recorded by Carstensen et al. (2014). This suggests that potential pollinators associated to Aspilia jolyana are more diverse than reported by both studies.

The most frequent visitor of A. jolyana, Bombus pauloensis, seems to be the most consistent pollinator of this generalist plant in the study area (Carstensen et al. 2016). This consistent interaction illustrates a link between two of the most generalist species in the community (Carstensen et al. 2014; 2016), which potentially has a key role in the entire plant-pollinator network. Besides the dominance of bees as visitors of A. jolyana, we also confirmed visits by other insect groups such as butterflies, wasps, flies and beetles (Carstensen et al. 2014). Nonetheless, we recorded legitimate visits by three species of hummingbirds not recorded before (see Tab. 1), indicating that A. jolyana is even more generalist than previously regarded. This reinforces the assertion that hummingbirds from open habitats in the Cerrado domain are rather generalist in their floral nectar use (Maruyama et al. 2013).

Pollinator visits significantly increased the seed set in A. jolyana although this plant can pollinate itself spontaneously. Likely, many visits are necessary during the life span of capitula for successful reproduction since florets mature sequentially. The difference on seed set between open and single visitation capitula also suggests that many visits are required for this plant to achieve maximum reproductive output. Thus, long-term viability of A. jolyana populations likely requires biotic pollination, although reproduction is assured in absence of pollinators. In this context, we showed that the most frequent bee species were equally effective in providing pollination. This also included the invasive honeybee, able to provide consistent pollination service by showing similar efficacy to native pollinators and ranked as the second most frequent visitor. Hence, at least in a generalist and morphologically non-restrictive flowers such as A. jolyana, we did not observe the expected differences on efficacy owed to differences on life-history and behavior between bees (see Westerkamp 1991). A previous study with another daisy, Heterotheca subaxillaris, conducted in meadows and grasslands in Central Texas, USA, also show similar efficacy of the most frequent visitors, and the overall relative effectiveness of pollinators is well represented by the visitation frequency of each pollinator (Olsen 1996).

There is much interest in comparing the efficacy and effectiveness of the honeybee to native pollinators in crop pollination (e.g. Freitas & Paxton 1998; Vicens & Bosch 2000) as well as in native plants (e.g. Fumero-Cabán & Meléndez-Ackerman 2007; Hung et al. 2018). Such studies have shown that A. mellifera can be as good pollinator as native species in both crops and native plants (e.g. Freitas & Paxton 1998; Rader et al. 2009; Fumero-Cabán & Meléndez-Ackerman 2007; Hung et al. 2018). However, A. mellifera is sometimes less effective than native species in commercial crops (e.g. Vicens & Bosch 2000) or even detrimental to the reproduction of the native flora in the invaded range (e.g. Gross & Mackay 1998). Here, our data indicated that A. mellifera was equally effective in promoting seed set as the native bees. Moreover, when considering the visitation frequency, the honeybee is one of the most important pollinators, second only to the native bumblebee B. pauloensis. Nevertheless, the presence of other frequent and effective pollinators of A. jolyana suggests that eventual removal of this invasive species would not negatively impact this plant as native bees are able to provide reliable pollination services.

Despite the effective role of invasive A. mellifera as pollinator of the generalist A. jolyana, the effect of this abundant floral visitor on the niche breadth and population sizes of the native social bees from the campo rupestre is still largely unknown. The few studies performed in the Neotropical region show little or no impact of Africanized honeybee in the populations of both social and solitary native bees (Roubik 2009; Roubik & Villanueva-Gutiérrez 2009). However, due to the scarce number of comprehensive studies, the literature does not allow any extensive generalization about the impact of A. mellifera introduction on the Neotropical bee fauna (Paini 2004).

In conclusion, we showed that frequent bee visitors, including several native species and the invasive honeybee, are equally good pollinators for a generalist daisy from the rupestrian grasslands. Aspilia jolyana showed high level of both ecological and functional generalization, conforming to its role as one of the species in the core of the local plant-pollinator network (Carstensen et al. 2016). The ability of A. jolyana to rely on different pollinators indicates resilience of its populations to possible fluctuations in the pollinator fauna, as well as diversified mating opportunities with different pollinators providing distinct pollen dispersal. All these characteristics suggest generalization as an interesting reproductive strategy.

Acknowledgements

We thank Daniel W. Carstensen for initial guidance and for sharing data. We also thank several members of the Phenology Lab group, UNESP Rio Claro for the logistical support and assistance in the field; the Reserva Vellozia and private land owners. Funding was provided by CNPq (400717/2013-1), São Paulo Research Foundation (FAPESP grant #2013/50155-0 to LPCM and grant #2015/21457-4 to PKM) and by CAPES through a PNPD Postdoctoral grant to CEPN. LPCM receives a research productivity fellowship from CNPq.

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Received: April 12, 2018; Accepted: May 09, 2018

* Corresponding author: pietrokiyoshi@gmail.com

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