Received: 18 May 2018 | Accepted: 18 August 2018 DOI: 10.1111/1365-2435.13204

RESEARCH ARTICLE

Flowers with poricidal anthers and their complex interaction networks—Disentangling legitimate pollinators and illegitimate visitors

José N. Mesquita‐Neto1,2 | Nico Blüthgen3 | Clemens Schlindwein1

1Departamento de Botânica, Universidade Federal de Minas Gerais, Belo Horizonte, Abstract Minas Gerais, Brazil 1. In flowers with poricidal anthers, pollen is not freely accessible and legitimate ac- 2 Laboratorio de Ecologia de Abejas, cess is restricted to bees capable of vibrating the anthers. Despite the protection Departamento de Ciências Biológicas y Químicas, Faculdad de Ciencias of pollen provided by poricidal anthers, numerous illegitimate, non‐buzz‐pollinat- Básicas, Universidad Católica del Maule, ing flower visitors rob pollen. Talca, Chile 2. We aimed to quantify the influence of functional groups of floral visitors and ille- 3Ecological Networks, Department of Biology, Technische Universität Darmstadt, gitimate interactions on the network structure to disentangle the flower visitor Darmstadt, Germany network into its mutualistic and antagonistic components. Correspondence 3. We delimited three functional groups of bees based on their pollen collection Clemens Schlindwein behaviour in poricidal flowers: large bees that vibrate entire flowers in a single Email: [email protected] buzzing position (flower buzzing), bees vibrating single anthers in different posi- Funding information tions (anther buzzing) and non‐vibrating flower‐damaging or gleaning bees (non‐ Rufford Foundation, Grant/Award Number: 17393-1; Fundação de Amparo à Pesquisa buzzing). Moreover, we characterized legitimate and illegitimate interactions of do Estado de Minas Gerais, Grant/Award co‐occurring and co‐flowering plants and their flower visitors based on the stigma Number: APQ-01707-14; Conselho Nacional de Desenvolvimento Científico contact during a visit. Since we independently assessed the type of interaction e Tecnológico, Grant/Award Number: PQ with bee–plant species combinations, we were able to include the behavioural 312831/2013-7; Instituto Chico Mendes de Conservação da Biodiversidade and variations of each bee species across different flowers. Instituto Estadual de Florestas de Minas 4. The networks were modular, with stronger interactions within subsets of species Gerais, Grant/Award Number: 120/2014; Coordenação de Aperfeiçoamento de than among the subsets. All modules included a combination of flower‐, anther‐ Pessoal de Nível Superior and non‐buzzing bees, and mutualistic and antagonistic networks were intermin- Handling Editor: Alison Brody gled. Seven bee species shifted their roles across plant species. Specialization in the subset of interactions with pollinators was higher than the overall visitation network. Flower‐buzzing bees were more specialized than anther‐buzzing and non‐buzzing bees, which used virtually all poricidal flowers similarly. 5. Although plants with poricidal anthers shared a specialized mechanism of pollen release, their pollinators were highly dissimilar and formed compartments of inter- acting species. The interaction‐level approach taken in our study confers a high specificity to the pollinator network, leading to a more complex and realistic pic- ture of mutualistic webs versus its embedded florivory, which are otherwise con- founded in pooled networks across flower visitors.

KEYWORDS bee‐plant interactions, buzz pollination, ecological Networks

Functional Ecology. 2018;1–12. wileyonlinelibrary.com/journal/fec © 2018 The Authors. Functional Ecology | 1 © 2018 British Ecological Society 2 | Functional Ecology MESQUITA‐NETO et al.

1 | INTRODUCTION (b) bees vibrating single anthers and (c) non‐vibrating flower‐damag- ing or gleaning bees. Pollen, one of the richest sources of protein produced by plants, The great diversity of buzz‐pollinated plants and their bee pol- is a valuable resource and motivation for to visit flowers linators in tropical regions offers an opportunity to characterize, in (Russell, Golden, Leonard, & Papaj, 2015). Pollen consumption or situ, the interactions between both groups. We conducted intensive collection is self‐motivated and not necessarily related to pollina- sampling of flower visitors to plant species with poricidal anthers tion (Hargreaves, Harder, & Johnson, 2009; Westerkamp, 1997a). To and defined the different functional groups of the bee species. This avoid excessive pollen loss, plants commonly present strategies to sampling design was chosen to avoid missing and forbidden links limit pollen consumption by floral visitors (Hargreaves et al., 2009; (Jordano, Bascompte, & Olesen, 2003; Olesen, Dupont, Hagen, Westerkamp & Claßen‐Bockhoff, 2007; Westerkamp, 1997b). In Trøjelsgaard, & Rasmussen, 2011) due to morphological constraints, flowers with poricidal anthers, pollen is not freely accessible and its spatio‐temporal uncoupling and phenological mismatching among removal requires buzz‐pollinating bees capable of anther vibration plants and flower visitors (e.g., phenophases of potentially interact- (Buchmann, 1974; De Luca & Vallejo‐Marín, 2013; Larson & Barrett, ing species do not overlap; species do not co‐occur in space or time). 1999a; Michener, 1962). This restriction of pollinators facilitates Thus, the numbers of interactions likely mirror the preferences of the evolution of floral adaptations that enhance pollination success the bees, including unobserved links that suggest that bees avoid (e.g., enantiostyly and heteranthery; Luo, Zhang, & Renner, 2008; plant species. Vallejo‐Marín, Silva, Sargent, & Barrett, 2010; Westerkamp, 2004). Here, we aimed to quantify the influence of functional groups Thus, poricidal plants possess a highly specialized and elaborate an- of floral visitors and illegitimate visits on network structure, disen- ther morphology, in which they protect and hide the pollen (Arceo‐ tangling a flower visitor network into its mutualistic and antagonis- Gómez, Martínez, Parra Tabla, & García‐Franco, 2011; Buchmann & tic components. We focused on the following questions: Do plant Hurley, 1978), and occur in non‐related plant lineages of 65 families species share flower visitors? How does network structure change and represent 8%–10% of angiosperms (Buchmann, 1983). if illegitimate visitors are included? Do different functional groups The floral constraint imposed by poricidal anthers benefits vi- of bee visitors also show different levels of specialization in their brating bees by reducing the number of competing pollinators (De interactions with plant species with poricidal anthers? We expected Luca & Vallejo‐Marín, 2013). Floral sonication probably arose in that, (a) plant species with poricidal anthers share pollinators due to a common ancestor of bees during Early Cretaceous and evolved their local co‐occurrence and overlap of flowering (Hypothesis 1); (b) about 45 times within bees (Cardinal, Buchmann, & Russell, 2018). illegitimate interactions show higher generalization than legitimate Possible bee pollinators able to collect pollen by anther vibration interactions because the behaviour of non‐buzzing bees on poricidal occur within the tribes Centridini, Euglossini, Xylocopini, Bombini flowers is not related to buzz pollination (Hypothesis 2). Thus, in- (), Augochlorini (Halictidae) and Caupolicanini (Colletidae) teraction legitimacy was independent of the functional roles. The (Buchmann, 1983; Michener, 1962), among others. Large‐sized bees, first is related to the consequences for plant reproduction and the in general, are recognized as effective pollinators of poricidal flow- second to the pollen collection behaviour. ers because they touch the stigma while buzzing flowers, remove more pollen per visit and intensely fly among conspecific plants (Buchmann & Hurley, 1978; Burkart, Schlindwein, & Lunau, 2014; 2 | MATERIALS AND METHODS Mesquita‐Neto, Costa, & Schlindwein, 2017; Renner, 1983; Solís‐ Montero & Vallejo‐Marín, 2017). 2.1 | Study site and plant species Despite the protection of pollen provided by poricidal anthers, numerous buzz‐pollinated plant species suffer pollen theft by Fieldwork was conducted in the “Parque Estadual do Rio Preto” na- small bees that do not vibrate flowers. These bees cut the anthers ture reserve in the municipality of São Gonçalo do Rio Preto, Minas or gnaw holes into them to remove pollen with their mouthparts Gerais State, Brazil (18°05’28.3"S, 43°20’29.2"W), from September (Gross, 1993; Rego, Oliveira, Jacobi, & Schlindwein, 2018; Renner, to December 2014 and 2015. The climate is tropical with dry (April– 1983). Other, usually small, bees pick up pollen grains adhering to September) and rainy (October–March) seasons and a mean annual the flower surface after visits of vibrating bees (e.g., Renner, 1983; temperature ranging from 15 to 35°C (Aw, Köppen’s ranking; Peel, Gross, 1993). Moreover, some small bees buzz only single anthers Finlayson, & McMahon, 2007). The vegetation of the reserve is and, in general, do not contact stigmas during their flower visits. All characteristic of the Cerrado (Brazilian Savannah). The study site is these flower‐visiting bees are non‐effective pollinators of plants characterized by sandy soil with a diversified plant cover composed with poricidal anthers (Gottsberger & Silberbauer‐Gottsberger, mainly of Melastomataceae, Fabaceae, Myrtaceae, Lythraceae, 1988; Gross, 1993; Hargreaves et al., 2009; Rego et al., 2018; Vochysiaceae, Eriocaulaceae, Cyperaceae, Xyridaceae and Poaceae, Renner, 1983; Solís‐Montero & Vallejo‐Marín, 2017; Solís‐Montero, among other families (IEF, 2004). Vergara, & Vallejo‐Marín, 2015). Thus, we can delimit three func- An intense sampling effort was done during the period of co‐ tional groups of bees based on their pollen collection behaviour in flowering of plants with poricidal anthers. We included plant spe- poricidal flowers: (a) large buzzing bees that vibrate entire flowers, cies in a radius of about 500 m from a given point (18°05’28.3"S, MESQUITA‐NETO et al. Functional Ecolo gy | 3

43°20’29.2"W). The criteria for choosing the sampling area was its bees: bees buzz the entire flower applying one or more buzzes; these richness of co‐flowering plant species with poricidal anthers. We bees vibrate all anthers in a unique position; (b) anther‐buzzing bees: selected 10 co‐flowering plant species from three families with bees buzz single anthers or a set of a few anthers of a flower; these poricidal anthers that were represented by at least 10 individuals at bees change their position in the flower between buzzes; (c) non‐ the site (Figure 1): Chamaecrista debilis (Vogel) H.S.Irwin & Barneby buzzing bees: bees collect pollen without buzzing the anthers; these (Fabaceae), shrub, up to 120 cm in height, yellow asymmetric flowers bees may collect pollen with their mouthparts, after cutting or per- (diameter 19 mm); Chamaecrista desvauxii (Collad.) Killip. (Fabaceae), forating anthers, or by gleaning residual pollen that adhered on dif- subshrub, up to 50 cm in height, yellow asymmetric flowers (diam- ferent floral parts after pollen extraction by vibrating bees. eter 29 mm); Comolia stenodon (Naudin) Triana (Melastomataceae), We independently assessed the functional role of a given bee subshrub, up to 50 cm in height, purple zygomorphic flowers (di- visit on a given plant species. During each flower visit, we noted the ameter 21 mm); Lavoisiera imbricata DC., shrub (Melastomataceae), pollen extraction behaviour (entire flower buzzing, single anther up to 150 cm in height, pink‐white zygomorphic flowers (diameter buzzing or non‐buzzing). Thus, the same bee species could show 19 mm); Leandra aurea (Cham.) Cogn. (Melastomataceae), shrub, up different functional roles during different visits on the same plant, to 60 cm in height, purple zygomorphic flowers (diameter 6 mm); and/or among different individuals of the same plant species and/or Macairea radula (Bonpl.) DC. (Melastomataceae), shrub, up to among different species. After the bee visits, we collected and killed 250 cm in height, pink‐white zygomorphic flowers (diameter 19 mm); the individuals to identify the species in the laboratory. When we Miconia albicans (Sw.) Steud. (Melastomataceae), shrub, up to 90 cm were not able to collect an observed individual bee, the data were in height, white zygomorphic flowers (diameter 9 mm); Pterolepis not considered. The interaction data were assembled into a quan- alpestris Triana (Melastomataceae), herb, up to 40 cm in height, pur- titative bipartite network using the bipartite package (Dormann, ple zygomorphic flowers (diameter 21 mm); Tococa guianensis Aubl. 2011; Dormann, Gruber, & Fründ, 2008) in R version 3.3.3 (R Core (Melastomataceae), shrub, up to 200 cm in height, white actinomor- Team, 2017). Each pairwise interaction frequency in the network phic flowers (diameter 15 mm); Ouratea floribunda Engl. (Ochnaceae), represents the number of visits of a given floral visitor to a poricidal shrub, up to 250 cm in height, yellow actinomorphic flowers (diam- plant species. The nodes of bee species were classified according to eter 17 mm). the three functional groups. To calculate the effect of each functional group of visitors on plant specialization, we compared the complementary specialization 2.2 | Functional groups of bees index (d′ index) of the plant species across the three subnetworks In 10 labelled plants per species, floral visitors were sampled and had (i.e., network that only includes flower‐buzzing, anther‐buzzing, their behaviour recorded on 25 sunny days in 2014 and 31 sunny or non‐buzzing interactions). The d′ index (Blüthgen, Menzel, & days in 2015, from 04:30 to 19:00 hr. A collector with an entomo- Blüthgen, 2006) describes each species’ deviation in flower visita- logical net remained for about 15 min at a single individual plant of a tion from the distribution of all visitors. High values, closer to 1, indi- species, sampling all flower visitors. After this time interval, the col- cate strong niche partitioning and specialization. We calculated the lector passed to another individual of another plant species and so mean d′ of all plant species, with each species being weighted by its on throughout the day. We performed a total of 672 hr of sampling total number of observations. effort with around 67 hr per plant species. A Generalized Linear Model (GLM) with quasibinomial distribu- We delimited three functional groups of visiting bees based on tion was constructed to search for any significant influence of visitor their pollen collection behaviour, according to Renner (1983), Solís‐ groups on variation in plant species d′. The GLM was calculated using Montero et al. (2015) and our own observations: (a) flower‐buzzing the stats package in R version 3.3.3 (R Core Team, 2017).

Chamaecrista desvauxii Chamaecrista debilis Comolia stenodon Lavoisiera imbricata Leandra aurea Macairea radula Miconia albicans Pterolepis alpestris FIGURE 1 Floral phenology of the Ouratea floribunda poricidal plants co‐occurring in the Tococa guianensis Rio Preto park in Cerrado, Brazil. Note that plants are co‐flowering during the JFMAMJJASO ND sampling period of our study (Sept–Dec) Flowering months 4 | Functional Ecology MESQUITA‐NETO et al.

were then used to calculate the z‐score, which is the number of 2.3 | Legitimate and illegitimate interactions standard deviations a datum is above the mean of the 100 random- In addition to pollen collection behaviour, we also noted if a bee con- ized networks using the functions r2dtable and vaznull in the bi- tacted the stigma during each flower visit. When a visitor touched partite package (Dormann et al., 2008). Z‐score values of ≥2 were the stigma, we considered the interaction legitimate, and illegitimate considered significantly modular (Dormann & Strauss, 2014). when it did not. We independently assessed the legitimacy of the The significance of the Connectance, Niche Overlap, Nestedness interaction for each bee–plant species combination, as we did to and H2′ were assessed by comparing the observed values to those evaluate the functional role (previous section). However, interaction obtained by 1,000 randomized networks generated by the null model legitimacy was independent of functional roles. The interaction legiti- r2dtable (Patefield, 1981) in the R‐package bipartite (Dormann et al., macy is related to stigma contact and functional roles to pollen col- 2008). We consider the r2dtable algorithm more adequate in our lection behaviour of bees. Thus, a same bee species can be legitimate study because it maintains the marginal totals and thus the total visitor of a given plant species and non‐buzzing bee, for example. number of observations per species (which directly limit the num- To simulate the effect of incorporating illegitimate interactions ber of links per species and most other metrics). This algorithm is on the set of interactions, we built two different bipartite networks widely used in other studies, making our results comparable to other grouping the interactions according to legitimacy: (a) the visitation pollination networks. Metric values were considered significant if network, including all flower visits, legitimate and illegitimate; and they did not overlap the 95% confidence intervals of the randomized (b) the mutualistic subnetwork, including only legitimate visits. values. Although no formal tests were conducted to compare the We evaluated variation in the network metric values and its sig- metric values across different types of interactions, which were im- nificance in relation to the null model. Thus, for the visitation and paired by the lack of replicates, these procedures are consistent with mutualistic networks, we calculated the following metrics to illus- those of previous studies, which compared subsets of interactions trate structural properties: (a) Connectance: the ratio between the (e.g.,illegitimate and legitimate visitors) of the same network (Genini, number of realized links to the number of possible links in the net- Morellato, Guimarães, & Olesen, 2010; Maruyama, Vizentin‐Bugoni, work; (b) Niche overlap: measure of similarity in interaction pattern Dalsgaard, & Sazima, 2015; Yoshikawa & Isagi, 2013). between species. Niche overlap was calculated using the Morisita– Horn index, which varies from 0 to 1 (Horn, 1966); (c) Nestedness: 2.4 | Species‐level analysis quantifies the chances of the network to present a nested pattern wherein specialists interact with proper subsets of the species in- We calculated z‐ and c‐values to describe the role of each species in teracting with generalists (Bascompte, Jordano, Melián, & Olesen, the modularity of the network (Guimera & Amaral, 2005; Olesen, 2003). We calculated the weighted nestedness using wNODF Bascompte, Dupont, & Jordano, 2007). The z‐value refers to (Almeida‐Neto & Ulrich, 2011); (d) Complementary specialization: within‐module and the c‐value to the among‐module connectivity, estimated by the H2′ index, which measures specialization in quan- which defines how the species is positioned within its own module titative networks (Blüthgen et al., 2006). Specialization and gener- and with respect to other modules. Following Olesen et al. (2007), alization were defined by the number of interactions established by we sorted all species into: (a) peripheral species (low z ≤ 2.5; low the species in relation to all possible interactions in the system. H2′ c ≤ 0.62), have few links inside its own module and rarely any to describes how much the interactions of each species differ from other modules; (b) module hubs (high z > 2.5; low c ≤ 0.62), species those of other species in the network, which has the advantage of that should be important for the coherence of their own modules; not being influenced by network size and number of observations (c) connectors (low z ≤ 2.5; high c > 0.62), species that should be per species (Blüthgen, Menzel, Hovestadt, Fiala, & Blüthgen, 2007); important for the coherence of their own modules; and (d) net- (e) Modularity: quantifying the prevalence of interactions within work hubs (high z > 2.5; high c > 0.62) should be important for the modules (i.e., subunits in the community), in relation to the inter- coherence of both the network and its own module. actions among modules. Weighted Modularity (Qw) was estimated using the QuanBiMo optimization algorithm (Dormann & Strauss, 3 | RESULTS 2014). This algorithm computes modules based on a hierarchical representation of species link weight and optimal allocation to 3.1 | Functional group level modules through swapping in a “Simulated Annealing‐Monte Carlo” approach (Dormann & Strauss, 2014). The level of modularity (Q) The poricidal plant flower visitor network at the study site com- measures the extent to which species interact mainly within their prised 584 interactions among nine poricidal plant and 55 bee module, ranging from 0 to 1. As the QuanBiMo algorithm is sto- species (Figure 2; Supporting Information Table S1). No floral chastic, the values found can be slightly different between runs; visitors were recorded on L. aurea flowers. Flower buzzing char- we accounted for this by choosing the higher values from 10 inde- acterized the majority of the interactions with poricidal plants pendent runs set to 107 swaps to each network (see, for example, (54.5%) followed by non‐buzzing (24.4%) and anther‐buzzing Maruyama, Vizentin‐Bugoni, Oliveira, Oliveira, & Dalsgaard, 2014; (24.1%) flower visits. Anther buzzing and non‐buzzing together Vizentin‐Bugoni et al., 2016). Values of Q in the randomizations accounted for 45.5% of the visits (266 visits). Non‐buzzing visits MESQUITA‐NETO et al. Functional Ecolo gy | 5

a

a

a

e

t

a

r

t

n

a

a

i

i

o

t

a

a

l

i

s

a

c

d

a

m

a

u

r

c

u

h

s

n

l a

t

a

l

a s

a

a

a

s

i

5

1 c

4 2

a

3 6

a

a

a

a

r

d

m

t

t

i

s

i

.

n

.

.

. .

f

.

s

e s

i

t

1

a

a

2 c

v

r

n

p

a i a

r

i

g

a

c

o

s

l

i

u

t

.

i

. i f

p

e

p

n a

p

p p

o

p

t

s

a

l

t

s

r

t

a

s

s

i

s r

r

t

n s

p

e

a

v

g

p

p

e

s

i

i

s

c

s

s

s s

v

s

a

o

u

c i

s

a

s n

r o

i

l

l

a

n

n

u

v

n a

i

a

1

n

o

d

c s

r

e

n

s

t

s

u

h

s

l

1

2 y

n

r

c

e

l

i

1

t

c

t

1

e e

o

.

s

a

.

u

a

r

o

e

s

e

e c

a

i

.

a

.

e e

l

.

o

a

a

q

t

i

a

o

e

u

s

s

s t

s

c

a

s

f

s

o

a

p

o

r

a

u

r

o

t

l

o

1

p

n

p c t

l

i

p

i

i i

i

l

i

i

r l

o s

p

b

t

r

p

i

d

b

p

a

p

i p

o

r

.

a n

l a

n

s

g

r

b

s

n

a

s

b

a

a

r

i

s r

e

s

a

i

a

h

i

s

s

s

s

e s

s

s

o h

u

s

t

t a

g

s

u

s

m

e

i

m

r

c

a

g r

s

p l

p

a

o

u

i

u n

g

r

u

o

e

s

f b

i

a

t

i

i

i

i t

c

n

c

o

.

e

n

u

i

p

p

p i

p

p

p

r

i

c

s

i

i

i

n

x

r

e

n

o

r

s

c

a

r

l

l

n

g

s

s

g

c

m f

a

b

m

.

c

h

b

n r

s

a

v

q

a

f

o

c

o

o

o n

o

a

o

o

i

s

o

p.1

p

e

a

a

a

e

f

e

a

a a

a

i

c

s

m p

g

e

e

r

r

r

r

r

r

r

r

a

u

l

n

i

a

g

p

g

s

s

l

n

n

d

t

l

p

f

c

a

c n

s s

v

t

s

a

r

a

a

a

o

o

o

o

a

a o

o

o

a

a

a

a

a a

a

a

s

o

n

f

a

u

a

l

l

l a

l

l

l

o

l

u

m

i

m e

o

o

o

s

s

e

l

s s

s

e

e

p

p

s

p

p

p

p

p

p

p

p

p

r

g

o

n

a

h

h

h

h

h

h

h

a

a

o

t

a

o

i

o

s

s

s

g

o

s

s

s

s

s

s

s

s

a

u u

u

s

o

o

m

s

m o

o

o

o l

o i

i

i

i

l

o

i

o

i o

i

i o

i

a

i

m

i

g

m

m

r

o

a

d

c

c

c

c

c

c

c

d

n

e

a

n

e

r

r

r

r

r

r

r

r

r

r

r

e

b

t

b

b

e

c

e

c

o

e c

c

g g

c

c

c

c

c

c

h

c

a

a

i

a

p

t

e

t

t

t

t

t t

t

t

t

i

t

o

o

o

o l o

o

o

u

m

o s

g

o

s

u

i

r

t

r

t

a

r

o

a

a

o

o

o

o o

o

o

o

o

l

o

c

o s

o

n

a

n

n

n

n y

n n

n

n

n

l

l

g

g l

l

g

g g g

g

g

l e

r

m

t l

r

l l

f o

r

m

l

g e l

y

l

l

m

l

i

l i

l

g

e

f

e

i i

i i

i

i

e

e

x

e

e x

e e

e

e

e

e

e

s

y

u

u

u u

y

u

u u u

u u

u

y s

a

o

e y

a

a

o

y

r y t t

x h

y

o

r

p

y

y p

r

y

y

r

u

T X

X

C

X

F O X

E T

C

M

B

E

C O T

A

A

E E X

X X

C C X A

C

A

C

C

A E A T A E

A

P

P

B

X P

C

P

B F

E

C P P

X

X

P

Macairea radula Miconia Ouratea Lavoisiera Pterolepis Comolia Chamaecrista desvauxii Chamaecrista Tococa guianensis albicans floribunda imbricata alpestris stenodon debilis

Buzzing flowers bees Buzzing single anther bees Non-buzzing bees (flower-buzzing) (anther-buzzing) (non-buzzing)

FIGURE 2 Bipartite network representing the interactions of poricidal plant species and bee visitors in Cerrado, Brazil. The bottom nodes (grey) representing the poricidal plant species and the upper coloured nodes represent the species of flower‐visiting bee. Links are coloured according to the bee functional group on flowers: flower‐buzzing bees (blue); anther‐buzzing bees (green); non‐buzzing bees (red). Note that visitor nodes with two colours are bee species that belong to different functional groups in different plant species were composed of 114 destructive visits (90.4%) and 11 gleaning 0.8 visits (9.6%). a Not all species of bees belonged to a single functional group. The species of Bombus spp., quinquefasciata, Augochloropsis sp. 0.6 4 and Pseudaugochlora pandora (nodes with two different colours in Figure 2) shifted their behaviour across different plant species. They 0.4

plants

’ b collected pollen by buzzing entire flowers (flower buzzing) in one

d species and by anther buzzing in another (see details in Species level). 0.2 After excluding flower‐buzzing interactions from the network, c the complementary specialization (d′ index) decreased signifi- cantly. Non‐vibrating bees reached the lowest d′ plants, close to 0.0 zero (Figure 3). Anther buzzing had a d′ index intermediate between Flower-buzzing Anther-buzzing Non-buzzing flower‐buzzing and non‐buzzing bees.

3.2 | Legitimate and illegitimate visits

Both the visitation network and the mutualistic subnetwork showed niche overlap and nestedness (NODF) lower than expected by FIGURE 3 Box plots of Complementary Specialization of plants chance (<95% lower confidence interval of the null model) and a (d′ index) related to functional groups of bees (flower‐buzzing, anther‐buzzing and non‐buzzing subnetwork). Different letters higher degree of complementary specialization H ′ (Table 1). In 2 indicate significant differences (p ≤ 0.01) by Generalized Linear addition, the networks were modular, with interactions stronger Model (GLM) with quasibinomial distribution within subsets of species than among subsets, although visitation and mutualistic networks contained plant species placed into dif- ferent modules (Figure 4). However, modularity increased in the All modules contained a mix of flower‐buzzing, anther‐buzzing and mutualistic subnetwork (Qw = 0.46) in relation to the visitation net- non‐buzzing bees, without apparent prevalence of one of the groups work (Qw = 0.36) with a higher z‐score (pollination network: r2d- (Figure 4). Flower‐buzzing, anther‐buzzing, and non‐buzzing bees table: 22.91; vaznull: 934.05; visitation network: r2dtable: 10.76; had legitimate visits, touching the stigma in 97%, 28% and 8% of all vaznull: 41.00) with more modules and higher H2′ (Figure 2; Table 1). visits, respectively. 6 | Functional Ecology MESQUITA‐NETO et al.

TABLE 1 Network metrics for the floral visitation network, in which all bee visits (legitimate and illegitimate) with poricidal flowers were included and for the mutualistic subnetwork, in which only legitimate visits were considered

Visitation network Mutualistic subnetwork

Observed index Observed index Network metrics value 95% lower CI 95% upper CI value 95% lower CI 95% upper CI

Niche overlap 0.23 0.56 0.61 0.25 0.52 0.54

H2’ 0.36 0.10 0.10 0.45 0.12 0.13 Weighted NODF 21.02 39.81 40.80 18.23 37.83 38.96 Connectance 0.29 0.40 0.41 0.28 0.41 0.42

Note. Metric values were considered significant if they did not overlap the 95% confidence intervals (CI) of the randomized values in 1,000 networks generated by the null model r2dtable. The networks are significantly non‐random when the CIs do not overlap with the observed values.

Tococa guianensis Comolia stenodon k Chamaecrista debilis Lavoisiera imbricata Chamaecrista desvauxii Ouratea floribunda Macairea radula Miconia albicans Pterolepis alpestris

r

r

s

s

s

s

s

s

s

s

s

s

s

s

5

a

a

1

6 2

a a a

1

a a

a

1 a a

a

a a

a

1

a

a

3

1

a

a

a

a

o

2

4 a

a

a

1

2

a

1

a

i

i

i

i

i

.

t

t

.

.

. .

t t

.

l t

. t i

i

t

.

t

t

.

.

t

t

i

.

.

t

.

.

i

r

r

o

o

l

l

i

n

n

e e

e

n

u

r

r

d

r

n

e

l

t

r

h

e

r

e

s

s

s

c

c

l

p

p

p p

r a

p

a

u

p m

a

p

a

p

i

a

p

p

a

i

a

p

p

a

p

p

e

o

a

a

l

l

i

t

i

a

i

e

l d

p

p

e i

t

c

f

a

a

o

r

a

n

o o

n

a

n

t

n

n

i

n

s

n

s

s s

s

s

s e

i

i

s

i

s

s

c

s

s i

s

s

s

g

i

h

i

d

r

i

v

s

s

c

c

c c

n

i u

l

c

d

v u

u

c

r

r

Visitation networ

n

p

a

e

a

v

n

e

e

s

e

l

p

o

p

n

t

i

t

o

m

n

o

i

c

s

s

s

s s

i

c

e

s

u

i

a

r

n

u

g

c

y

a

m

o

o

r

f

a

i

o

s

s s

s

s

o

s

u

s

a

a

a

e r

a

n

o

l

a

a

b

a

o

t

a

a

l

v

t

a

r

x

i

o

i i

a

e

i

l

i

e a

f

i

r

a

t

u

g

s

p

a

c

t

r

n

i

n

a

b

g

f

f

f

r

t

u

i

c

t

n

b

n

o

i

r

a

n

s

n

n

n

i

e

s

r

s s

u

r s

p

s

s

v

e

s

a

i

s

u

i

m

n

r

e

m

b

a

o

e

p

s

i

r

l

e s

s

o

l

m

g

m

t

c

c

s

s

l

e

o

b

o

g

o

u

i

o

a

o

s

n

c

g

p

p p

a

r

p

p

a

s

p

p

i

i

a

c

i

i

t

a

i s

l

u

d

r

r

l

i

v

e

u

e

a

n

e

r

b

r

m

h

a

g

g

r

b

t

g

i

c

f

l

o

o

o

g

a

o

o

r

o

b

n

s

a

p

t

t

s

a

i

i

t

a

m

m

e

i

s

t

a

r

r

r

i

q a

r

r

r

r

p

c

a

e a .

a

e

r

r

n

s

r

h

i

a

s

u

m

m

r

f

n

a a

s

.

n

g

s a

t

m

a

a

i

t

i

f

r

n

o

o

o

p

p

n

o

o

o

l

o

o

o

p i

t

r

h

t

m

a

a

e

r

T

a

t

a

e

r

l

l

l

o

i

C

c

a

l

l

l s

s

l

o

o

a

a

y

c

y

m s

o

p

a

e

l

r

r

o

r

t

a

t

l

e

c

o

i

c

g

o t

g

A p

s

r

a

p

n

e

h

h

h

e s

u x

p

h

h

u

h

o

i

h

e

p

p

h

r

e

g

o

C

p

u

a

s

a

n

n

h

i

c

B

l

C

o

c

t

i

a

u

n

i

a

o

e

C

a

c

c

c

s

p

o

s

e

c

c

c

a

c

s

l

q

o

b

c

p

o

o

a

r

o

T

i

e

c

O

i

e

E

n

o

s

g

P

P

o

l n

s s

s

c

e

c

x

r

o y

o

A

o

e

o

l r

c

o

o

o

o

e

c

c

l

o

P c

C

T

f

E

o

i

t

s

i

o

m

l

o

s

u e

p u

C

o

C

c

o

y

g

g

g

y

r

o

g

g

g

l

g

r

o

o

C

a

o

X

l

O

l

u

g

n

l

y

o

i

l

l

g

o

o

l

o b

o

E

l

t

u

u

u

C

u

u

u

u l

y

F

n X

l

F

X

y

l

y

u

y

y

e

y

a

E

X

B

g

a

g

r o

m

P

a

A

A

A

y

A

A

A

X

a

X

t

X

X

X

X

C

o

d

u

p

o

l

d

X

e i

m

i

l

u

t

E

B

u

o

T

e

e

e

x

P

s

s

M

E

P

P

Miconia albicans

k Ourateafloribunda Tococa guianensis

Chamaecrista desvauxii Macairea radula

Comolia stenodon Pterolepis alpestris Chamaecrista debilis

Lavoisiera imbricata

r

s s

s

s

s

s s

s

s

a

a

a a

a

a

a a

a

a

a

a

6

a a a

a

a a a

4 a

o

1

a

.

i

i

i

i

t

i

t

t

i

i .

t t

t

t

t t t

. t i

o

r

l

e

n

e u

n

i

e

e d

r

h

n

r r

t

r

r

p

s

s

s

l

c

c

a

m

a i

i

p

a

a r a

p

a

a

o

l

a

d

i

c

t e

p

e

i

l

i

l

n

n o

a

r

a

a

a

o No. of visits s

n

i

n

t

n

c

i

i

s i

n

s

s e

h

g

Mutualistic networ

r

d

s

c

c

v

i

c

v

r

u

c

i u

r

u

e

a p

a

n

v

s

e

e

n

e

o

t

t

p

p

o

m

o

i

n

i

s

s

s

c

s

s

r

s

e

c

y

c

n g

a

a

o

o f r

i

u

s

s s o

o

n

o

l a

o

t

r

l

v

x

t

r

a

f

e

i

e

o

i

l a

u

c

s

a

u

r

a

i

n

b g

f

i

c

u

r high f

o

n

a

i

s b

i low e

a

u

s

r e

s

v

s

p

u

b

b

r

m

e

s

p

a

i

r

s

s

e

t

c

m

c g

s

m

i

g

a

u b

c

s

n

s

r

a p

p

a

p

c

i

i

a

i

u s

i

l

r

i

r

l

a

u

b

m

n

e

r

a

t

r

b a m

i

c

f

r

g

o

o

r

s

t

n

t

p

b

t

e

a

t

s

r

a

r

q

o

e

.

a

a

p

n

s

e

h

s

a

i

o

f

a

a s

.

n

i

m

i

n

r

l

l

o

p

o

n

m

p

r

o

e

r

a

a

B

r

a

t

a

e

C

c

a

s

l

l

s i

a

s

p

m a

e

a

t

o

l

t

e

h

i

o

c

o

g

s

p

a

p

n

e

p

o

h

h

u u

p C

r

o

e p

p

n

u

n

c

l

c

B

C

t

a

c

o

a

C

e

o

s

p

o

e

a

c

c

o

c

l b q

o

o

a

o

e

i

i

e

o

s

g

o

E

n

s

o

s

l

c

c

x

r

r

o

c

l

o

o y

c

o

l

c

c

C

f

t

g

s

s

l

o

m

e C

u

u

C

o

c

o

y

o

l

y g

g

o

o

a

o

O

X l

l

u

u

n

o

l

y

i

l

o

l

o

l

b

o

l

t

E

C

l

u

u

X

y n

y

X

l

y

a

y

e

y

y

E

X

B

g

g

P

m

o

y

A

A

X

d

X

X

X

X

X

C

o

u

o

p

l

u

X

i

i

l

E

t

B

e

e

s

P

M

P

FIGURE 4 Modules in the poricidal plant–bee visitor network from Rio Preto Park, Cerrado, Brazil. The top matrix, the entire visitation network, includes all interactions; the bottom matrix, mutualistic subnetwork, excludes illegitimate interactions. The visitation network was modular (Qw = 0.36) and with a “high” z‐score (r2dtable: 10.76; vaznull: 41.00). However, modularity increased in the mutualistic subnetwork (Qw = 0.46), with a higher z‐score (r2dtable: 22.91; vaznull: 934.05). Note that the number of modules and their compositions varies among the networks

The submodules in the mutualistic network (Figure 4, blue species had only one legitimate visitor species each in their sub- squares) revealed which plant species had a set of more related modules (C. debilis, M. albicans and L. imbricata). Three other spe- legitimate visitors (Figure 4). However, the number of legitimate cies had two to four legitimate visitor species in their modules visitors in these sets varied among plant species. Three plant (C. stenodon, P. alpestris and T. guianensis). Chamaecrista desvauxii, MESQUITA‐NETO et al. Functional Ecolo gy | 7

M. radula and O. floribunda had five or more legitimate visitor species. Flower‐buzzing bees made up most of the mutualistic part- species. ners of poricidal plants. These bees had many more legitimate visits than anther‐buzzing and non‐buzzing bees, and were more faith- ful to a subset of plant species, and thus more likely to promote 3.3 | Species level cross‐pollination. Most bee species in the visitation network (83%) had low within‐ module (z) and among‐module (c) connectivity values, meaning that 4.1 | Subsets of interacting species they showed preference to distinct poricidal species with few links, mostly within their module (peripheral roles). Only nine of the 55 Because plants with poricidal anthers require a common mechanism bee species were generalist species (interactions with many plants to extract pollen, we supposed that these plants would share polli- with poricidal anthers), with either high z‐ or c‐values (Figure 5). nators. However, our results show that the pollinators of these plant Most generalists were connector species (low z, high c) that link species are dissimilar and overlap only partially. Our network was modules but which belong to none. None of the non‐buzzing bees characterized by modular interactions. Modules exist because some was a connector (Figure 5). Augochloropsis sp. 4 was identified as a species do not interact or interact less with certain species in the module hub species, with many links within‐modules (high z) and few community (Dormann & Strauss, 2014). The modules of the mutu- among‐modules (high c). Trigona sp. 1 and M. quinquefasciata were alistic subnetwork include a range of shared pollinators among few visitation network hubs (high c and z). Trigona sp. 1, an illegitimate poricidal plants. Besides, each plant species is in a different submod- visitor, damaging anthers without contacting the stigma, interacted ule, with its own core of pollinators. Thus, only a subset of all possible with most plant species (8 spp.) and was responsible for the major- buzzing bees interacts with certain plant species. Other co‐flower- ity of interactions with flowers of the different plant species in the ing species, like those of the genera Acacia, Avicennia, Laguncularia, visitation network (Figure 2). Ipomoea, Ophrys and Vigna, also avoid pollinator sharing (Gögler et The mutualistic network did not show network hubs, but the pro- al., 2015; Landry, 2012; Matsumoto et al., 2015; Queiroz, Quirino, portion of specialist bee species was similar to the visitation network & Machado, 2015; Souza, Snak, & Varassin, 2017; Stone, Willmer, & (85%). Five species were generalists, and the two Bombus species Rowe, 1998). Pollination efficiency should decrease when flowers of showed single anther buzzing in other plant species. Two species different plant species are visited by the same pollinator species in were module hubs (Bombus morio, Centris fuscata) and three were the same period, leading to a reduction in flower visitation rates for connectors (B. pauloensis, C. tarsata, Euglossa melanotricha; Figure 5). each plant species (Fishbein & Venable, 1996; Waser & Fugate, 1986; Bombus spp., M. quinquefasciata, Augochloropsis sp. 4 and P. pan‐ Waser, 1978a, 1978b) and to heterospecific pollen flow (Ashton, dora had varied roles in flowers. Their buzzing behaviour and legit- Givnish, & Appanah, 1988). Thus, the vibration requisite is not the imacy of interactions differed in different plant species. The bees ultimate specialization barrier of poricidal plants. Additional inter- were flower buzzing in certain plant species but anther‐buzzing in specific features of the flowers, such as differences in the amount of others. Bombus brevivillus, B. morio and B. pauloensis were flower pollen, floral colour, position, size or shape, and/or morphological/ buzzing in most plant species, except C. desvauxii, L. imbricata and behavioural characteristics of the bees such as differences in buzz- T. guianensis. However, the species of Bombus touched the stigma of ing characteristics (frequency, amplitude, duration), flower handling all plant species in most visits (legitimate visitors). Bees of M. quin‐ time or bee size, may mediate the interactions and segregate pollina- quefasciata showed anther buzzing in flowers of almost all species, tors among the co‐flowering species with poricidal anthers. but flower buzzing only in the flowers of O. floribunda. However, Future studies can search for the floral traits and bee character- M. quinquefasciata touched the stigma in most visits, except in T. gui‐ istics that may modulate their interactions. Buzzing bees can adjust anensis. Bees of Augochloropsis sp. 4 showed flower buzzing and their foraging behaviour and adopt different strategies to maximize were legitimate flower visitors only in M. albicans. In most plants, resource extraction in a subgroup of plant species (Burkart et al., Augochloropsis sp. 4 was an anther‐buzzing bee. P. pandora visited 2014; Corbet & Huang, 2014; Russell et al., ; Switzer, Hogendoorn, mainly C. desvauxii but was a legitimate visitor only in flowers of Ravi, & Combes, 2016). Thus, it is likely that each buzzing bee spe- O. floribunda (See Figure 1; Supporting Information Table S1). cies chooses the most rewarding flowers, relative to their buzzing range, in order to increase pollen release while reducing buzzing ef- fort (Buchmann & Cane, 1989; Harder, 1990; Russell et al., ). New 4 | DISCUSSION studies can test if the choice by bees of the most rewarding plants, within their buzzing range, is one of the selective forces generating Although the poricidal co‐occurring and co‐flowering plant spe- modules of interacting species and specialization in the network. cies require a common specialized mechanism of pollen extraction, their pollinators were highly dissimilar and formed compartments 4.2 | The role of flower‐buzzing bees of interacting species. As expected, the specialization of the sub- set of mutualistic interactions was higher than the overall visita- Flower‐buzzing bees had much more specialized interactions tion network and constrained pollinators to one or a few per plant with poricidal flowers, a typical feature of pollination networks, 8 | Functional Ecology MESQUITA‐NETO et al. particularly those of bees (Danieli‐Silva et al., 2012; Fründ, Linsenmair, network. Anther‐buzzing bees are intermediates; they are less spe- & Blüthgen, 2010; Renner, 2007). Functionally specialized, the be- cialized and effective pollinators than flower‐buzzing bees, but more haviour of flower‐buzzing bees on flowers is more likely to promote efficient pollinators than non‐buzzing bees. Anther‐buzzing bees pollination. While buzzing flowers, these bees contact the stigma in spent more time in the flowers to apply vibrations on anthers indi- most visits because their body size usually exceeds the gap between vidually, but contact stigmas more rarely and are not very effective anthers and stigma (see Liu & Pemberton, 2009; Solís‐Montero & pollinators of plant species with poricidal anthers (also see Luo, Gu, & Vallejo‐Marín, 2017). Flower‐buzzing bees, like those of Bombini, Zhang, 2009; Liu & Pemberton, 2009; Renner, 1983; Wanigasekara Centridini, Euglossini and Xylocopini effectively adjust pollen‐col- & Karunaratne, 2012). lecting behaviour to quickly extract large amounts of pollen from Antagonistic interactions of the abundant non‐buzzing bees poricidal anthers (Buchmann, 1983; Buchmann & Hurley, 1978; added generalization to the network due to their indiscriminate vis- Burkart et al., 2014; De Luca et al., 2013; Renner, 1983; Russell, its to flowers of all species. Non‐buzzing bees are opportunistic and Buchmann, & Papaj, 2017). Almost all these bee species were net- better connected; they used virtually all flowers similarly. Flowers work peripherals and visit flowers of a few plant species. If this is were left visually damaged after destructive visits of non‐buzzing true, the absence of any flower‐buzzing bee species may affect the bees. The destructive visits of non‐buzzing Trigona bees compro- reproductive success of one or of a set of plant species because mise pollination of plants with poricidal anthers because they re- they might be key pollinators in the system. A direct consequence of duce the visual attractiveness of the flowers to effective pollinators the decline of flower‐buzzing bee species would be the decrease in (Hargreaves et al., 2009) and can directly cause negative impacts cross pollen flow. A short‐time consequence might be that the less on the reproductive success of their host plants (Rego et al., 2018). efficient anther‐buzzing and non‐buzzing bee species could exploit Bees of this genus are widespread and frequently cited as destruc- more intensively these flowers, occupying the empty niches left by tive flower visitors (Biesmeijer & Slaa, 2006; Gross, 1993; Rego et missing flower‐buzzing bees. al., 2018; Renner, 1983; Schlindwein, Westerkamp, Carvalho, & Milet‐Pinheiro, 2014). Although these bees extract pollen less effi- ciently, they are numerous in poricidal flowers and must be import- 4.3 | Illegitimate interactions add generalization ant competitors for flower‐buzzing bees in flowers with poricidal to the network anthers. In our study, the non‐buzzing Trigona bees were even the Anther‐buzzing and non‐buzzing bees were responsible for most visitation network hub and most common flower visitors. Thus, the illegitimate interactions, which increased the generalization of our frequency of visits in flowers alone is not a sufficient parameter for

Visitation

N Mutualistic

N

3 e 3 Augochloropsis Melipona quinquefasciata Centris fuscata e

sp.4 t

t

w

)

w

) Module hubs Trigona sp.1 Module hubs Bombus morio C

e

o

e

o

r o

e

e Centris fuscata r

k

r

k

r Pseripheral Connectors Pseripheral n

g

g

h n

h

e

u Bombus morio e e 2 2 u

b c

d

d

b t

s

s o

e

e

l

l

Centris tarsata Bombus pauloensis r s

u u Eulaema cingulata

d d Eulaema nigrita Bombus pauloensis Eulaema nigrita o o 1 Eulaema cingulata Augochloropsis sp.6 1 Centris varia Xylocopa nigrocincta

m m Bombus gr. brevivillus Pseudaugochlora pandora

- - Pseudaugochlora graminea Xylocopa muscaria Oxaeaflavescens

n n Xylocopa nigrocincta Pseudaugochlora pandora

i i Augochloropsis sp.3 Augochloropsis sp.4

h h Augochloropsis sp.1 Bombus gr. brevivillus

t t Centris varia Xylocopa abbreviata

i i Oxaeaflavescens Augochloropsis sp.6 Xylocopa bimaculata w Centris cf. spilopoda Centris tarsata w 0 Xylocopa muscaria Eufriesea nigrohirta 0 Xylocopa frontalis

( ( Eufriesea nigrohirta Augochlora Trigona spinipes Euglossa melanotricha Centris trigonoides Xylocopa abbreviata

sp.1 s s Apis mellifera Xylocopa bimaculata Euglossa melanotricha

e e Augochloropsis sp.5 Centris perforator Xylocopa cearensis

u u Centris perforator

l l Centris caxiensis Partamona sp.1 Xylocopa carbonaria

a Xylocopa cearensis a Xylocopa grisescens

–1 v –1 v Xylocopa subcyanea Augochloropsis sp.2 Xylocopa subcyanea

- Centris aenea Xylocopa frontalis

Xylocopa suspecta z Centris caxiensis z- Centris aenea Xylocopa suspecta Thygater analis Melipona quinquefasciata Centris scopipes Exomalopsis fulvofasciata Centris scopipes –2 –2 00.1 0.20.3 0.40.5 0.60.7 0.8 00 .01 .02 .03 .04 .05 .6 0 .7 c-values (among-module degree) c-values (among-module degree)

Flower-buzzing Anther-buzzing Non-buzzing Flower/Anther-buzzing

FIGURE 5 Bees visiting poricidal plants categorized according to within‐module (z‐value) and among‐module (c‐value) connectivity: (a) peripheral species: with few links inside its own module and rarely any to other modules; (b) module hubs: important to the coherence of its own module; (c) connectors: important to the coherence of its own module; (d) network hubs: important to the coherence of both the network and its own module. Bee nodes in the visitation graphic (left) are coloured according to bee functional group: (a) flower‐buzzing bees: bees buzzing all the anthers in a flower at once; (b) anther‐buzzing bees: bees buzzing a single or set of anthers in a flower; (c) non‐ buzzing bees; (d) Flower/anther‐buzzing bees: bees with two roles in different plants species (flower buzzing and anther buzzing). In the mutualistic graphic (right) only flower‐buzzing visits are considered MESQUITA‐NETO et al. Functional Ecolo gy | 9 understanding the biological role of Trigona in our network and it interactions with poricidal flowers than buzzing bees (Hypothesis could instead, lead to misinterpretations. 2). Thus, the distinction of antagonistic flower visitors and mutual- istic partners, and other aspects of the evolutionary history of the partners (see Renner, 2007), may have implications for generalization 4.4 | Buzzing bees shifted their roles across flowers and specialization approaches of plant–pollinator interactions. While Medium‐sized bees of Augochloropsis, Pseudaugochlora, Melipona, the majority of angiosperms appear to be pollinated by a great range and Bombus workers were flower buzzing in plant species were they of taxa (Ollerton, 1996; Waser, Chittka, Price, Williams, & Ollerton, contacted stigmas and anther buzzing in others where they gener- 1996), this high level of observed generalization may be partially a ally did not contact stigmas. Thus, the same bee species can be mu- consequence of the incorporation of antagonistic interactions on the tualist of a certain plant species and make floral larceny in another. set of mutualistic ones. Since we independently assessed the interac- However, these bees were never observed cutting anthers or picking tion type for bee–plant species combinations, we were able to include up pollen from the flower surface. the dynamic functions of each bee species across different flowers. The relationship between bee size and the distance between The interaction‐level approach taken in our study confers a high spec- anthers can influence the buzzing behaviour of a bee in a flower, as ificity to the pollinator network, leading to a more complex and real- well as its efficiency as a pollinator (Solís‐Montero & Vallejo‐Marín, istic picture of mutualistic webs versus its embedded florivory, which 2017). In actinomorphic Solanum‐type flowers (Buchmann, 1983; are otherwise confounded in pooled networks across flower visitors. De Luca & Vallejo‐Marín, 2013; Vogel, 1981), stamens are grouped to a cone and anther pores are close to each other. In these flow- ACKNOWLEDGEMENTS ers, smaller bees can also vibrate all anthers at once, and bees are efficient pollinators when their body size exceeds the gap between We thank Rosana Romero, Universidade Federal de Uberlândia, for anthers and stigma (Solís‐Montero & Vallejo‐Marín, 2017). In our identifying the plants and Felipe Vivallo, Universidade Federal do Rio study, two medium‐sized bee species are among the main pollina- de Janeiro, and Fernando Silveira, Universidade Federal de Minas tors of O. floribunda that fit the Solanum‐type flower but are anther‐ Gerais, for identifying the bees, Stephen Buchmann and an anony- buzzing non‐pollinators in the zygomorphic flowers of Chamaecrista mous reviewer for their constructive comments, which improved the and Melastomataceae, which have stamens distant from each other. manuscript. Licences for collecting were granted by Instituto Chico We are aware that restricting the stigma contact of a bee during a Mendes de Conservação da Biodiversidade and Instituto Estadual de flower visit to access its legitimacy is a simplified measure with limited Florestas de Minas Gerais [No. 120/2014]. This work was supported explanatory power and can lead to misinterpretations. In the field, it by Fundação de Amparo à Pesquisa do Estado de Minas Gerais is not practicable to verify if a given bee individual has deposited con- [APQ‐01707‐14]; Coordenação de Aperfeiçoamento de Pessoal de specific pollen grains on the stigma without removing the stigma and Nível Superior [Scholarship to J.N.M.-N.]; Conselho Nacional de analysing it under the microscope. In plants with poricidal anthers, Desenvolvimento Científico e Tecnológico [Scholarship to J.N.M.-N. pollen deposition on the stigma may eventually occur even without and to C.S.]; and The Rufford Small Grants Foundation [No. 17393‐1]. the body contact of the buzzing bee to the stigma, allowing fruit set in self‐compatible species. On the other hand, in mass‐flowering self‐ AUTHORS' CONTRIBUTIONS incompatible species, floral visitors may contact many stigmas in the same plant, leading to an increase in geitonogamy and a decrease J.N.M.-N. and C.S. conceived the ideas and designed methodol- in fruit set (de Jong, Waser, & Klinkhamer, 1993; Pinto, Oliveira, & ogy; J.N.M.-N. collected the data; J.N.M.-N. and N.B. analysed the Schlindwein, 2008; Schlindwein et al., 2014). However, in community data; J.N.M.-N. and C.S. led the writing of the manuscript. All au- studies with a large set of interactions, like here, stigma contact ap- thors contributed critically to the drafts and gave final approval for pears to be a powerful simplified measure to filter legitimate flower publication. visits. In addition, the legitimacy of a bee species was based on a set of independent observations with a given plant species. DATA ACCESSIBILITY We conclude that plant species with poricidal anthers in co‐oc- currence and co‐flowering share pollinators, however, subgroups of All data are publicly available in the Figshare Repository (Mesquita‐ plant species have a set of interacting pollinators. Although non‐buzz- Neto, Blüthgen, & Schlindwein, 2018; https://doi.org/10.6084/ ing bees are network hubs, they contribute little or even negatively m9.figshare.6073598). to pollination of species with poricidal anthers and were responsible for most antagonist interactions. Among the bees that remove pol- len by vibration, the flower‐buzzing bees are the most specialized ORCID and efficient pollinators. Differing from our prediction (Hypothesis José N. Mesquita‐Neto https://orcid.org/0000-0002-1519-638X 1), co‐occurring and co‐flowering plant species with poricidal anthers only partially share pollinators and have modules of interacting spe- Nico Blüthgen https://orcid.org/0000-0001-6349-4528 cies instead. As predicted, non‐buzzing bees have less specialized Clemens Schlindwein http://orcid.org/0000-0002-9947-3902 10 | Functional Ecology MESQUITA‐NETO et al.

REFERENCES De Luca, P. A., & Vallejo‐Marín, M. (2013). What’s the “buzz” about? The ecology and evolutionary significance of buzz‐pollination. Current Almeida‐Neto, M., & Ulrich, W. (2011). A straightforward computa- Opinion in Plant Biology, 16, 429–435. https://doi.org/10.1016/j. tional approach for measuring nestedness using quantitative ma- pbi.2013.05.002. trices. Environmental Modelling & Software, 26, 173–178. https://doi. Dormann, C. F. (2011). How to be a specialist? Quantifying specialisation org/10.1016/j.envsoft.2010.08.003. in pollination networks. Network Biology, 1, 1–20. Arceo‐Gómez, G., Martínez, M. L., Parra Tabla, V., & García‐Franco, J. Dormann, C. F., Gruber, B., & Fründ, J. (2008). Introducing the bipartite G. (2011). Anther and stigma morphology in mirror‐image flow- package: Analysing ecological networks. R News, 8, 8–11. ers of Chamaecrista chamaecristoides (Fabaceae): Implications Dormann, C. F., & Strauss, R. (2014). A method for detecting modules in for buzz pollination. Plant Biology, 13, 19–24. https://doi. quantitative bipartite networks. Methods in Ecology and Evolution, 5, org/10.1111/j.1438-8677.2010.00324.x. 90–98. https://doi.org/10.1111/2041-210X.12139. Ashton, P. S., Givnish, T. J., & Appanah, S. (1988). Staggered flowering Fishbein, M., & Venable, D. L. (1996). Diversity and temporal change in the Dipterocarpaceae: New insights into floral induction and the in the effective pollinators of Asclepias tuberosa. Ecology, 77, 1061– evolution of mast fruiting in the aseasonal tropics. The American 1073. https://doi.org/10.2307/2265576. Naturalist, 132, 44–66. https://doi.org/10.1086/284837. Fründ, J., Linsenmair, K. E., & Blüthgen, N. (2010). Pollinator diversity and Bascompte, J., Jordano, P., Melián, C. J., & Olesen, J. M. (2003). The specialization in relation to flower diversity. Oikos, 119, 1581–1590. nested assembly of plant– mutualistic networks. Proceedings https://doi.org/10.1111/j.1600-0706.2010.18450.x. of the National Academy of Sciences of the United States of America, Genini, J., Morellato, L. P. C., Guimarães, P. R., & Olesen, J. M. (2010). 100, 9383–9387. https://doi.org/10.1073/pnas.1633576100. Cheaters in mutualism networks. Biology Letters, 6, 494–497. https:// Biesmeijer, J. C., & Slaa, E. J. (2006). The structure of eusocial bee assem- doi.org/10.1098/rsbl.2009.1021. blages in Brazil. Apidologie, 37, 240–258. https://doi.org/10.1051/ Gögler, J., Stökl, J., Cortis, P., Beyrle, H., Lumaga, M. R. B., & Cozzolino, S. apido:2006014. (2015). Increased divergence in floral morphology strongly reduces Blüthgen, N., Menzel, F., & Blüthgen, N. (2006). Measuring specializa- gene flow in sympatric sexually deceptive orchids with the same pol- tion in species interaction networks. BMC Ecology, 6, 9. https://doi. linator. Evolutionary Ecology, 29, 703–717. https://doi.org/10.1007/ org/10.1186/1472-6785-6-9. s10682-015-9779-2. Blüthgen, N., Menzel, F., Hovestadt, T., Fiala, B., & Blüthgen, N. (2007). Gottsberger, G., & Silberbauer‐Gottsberger, I. (1988). Evolution of flower Specialization, constraints, and conflicting interests in mutualistic structures and pollination in Neotropical Cassiinae (Caesalpiniaceae) networks. Current Biology, 17, 341–346. https://doi.org/10.1016/j. species. Phyton (Austria), 28, 293–320. cub.2006.12.039. Gross, C. L. (1993). The breeding system and pollinators of Melastoma Buchmann, S. L. (1974). Buzz pollination of Cassia quiedondilla affine (Melastomataceae); A pioneer shrub in tropical Australia. (Leguminosae) by bees of the genera Centris and Melipona. Bulletin of Biotropica, 25, 468–474. https://doi.org/10.2307/2388870. the Southern California Academy of Sciences, 73, 171–173. Guimera, R., & Amaral, L. A. N. (2005). Cartography of complex Buchmann, S. L. (1983). Buzz pollination in angiosperms. In C. E. Jones, networks: Modules and universal roles. Journal of Statistical & R. J. Little (Eds.), Handbook of experimental pollination biology (pp. Mechanics: Theory and Experiment, 2005, P02001, https://doi. 73–113). New York, NY: van Nostrand Reinhold Company. org/10.1088/1742-5468/2005/02/P02001. Buchmann, S. L., & Cane, J. H. (1989). Bees assess pollen returns while Harder, L. D. (1990). Behavioral responses by bumble bees to variation sonicating Solanum flowers. Oecologia, 81, 289–294. https://doi. in pollen availability. Oecologia, 85, 41–47. https://doi.org/10.1007/ org/10.1007/BF00377073. BF00317341. Buchmann, S. L., & Hurley, J. P. (1978). A biophysical model for buzz pol- Hargreaves, A. L., Harder, L. D., & Johnson, S. D. (2009). Consumptive lination in angiosperms. Journal of Theoretical Biology, 72, 639–657. emasculation: The ecological and evolutionary consequences https://doi.org/10.1016/0022-5193(78)90277-1. of pollen theft. Biological Reviews, 84, 259–276. https://doi. Burkart, A., Schlindwein, C., & Lunau, K. (2014). Assessment of pollen org/10.1111/j.1469-185X.2008.00074.x. reward and pollen availability in Solanum stramoniifolium and Solanum Horn, H. S. (1966). Measurement of "overlap" in comparative ecologi- paniculatum for buzz‐pollinating carpenter bees. Plant Biology, 16, cal studies. The American Naturalist, 100, 419–424. https://doi. 503–507. https://doi.org/10.1111/plb.12111. org/10.1086/282436. Cardinal, S., Buchmann, S. L., & Russell, A. L. (2018). The evolution of flo- IEF ‐ Instituto Estadual De Florestas. (2004). Plano de Manejo do Parque ral sonication, a pollen foraging behavior used by bees (Anthophila). Estadual do Rio Preto. Curitiba: IEF. Evolution, 72, 590–600. https://doi.org/10.1111/evo.13446. Jordano, P., Bascompte, J., & Olesen, J. M. (2003). Invariant properties Corbet, S. A., & Huang, S. Q. (2014). Buzz pollination in eight bumble- in coevolutionary networks of plant‐animal interactions. Ecology bee‐pollinated Pedicularis species: Does it involve vibration‐induced Letters, 6, 69–81. https://doi.org/10.1046/j.1461-0248.2003. triboelectric charging of pollen grains? Annals of Botany, 114, 1665– 00403.x. 1674. https://doi.org/10.1093/aob/mcu195. Landry, C. L. (2012). Pollinator‐mediated competition between two Danieli‐Silva, A., de Souza, J. M. T., Donatti, A. J., Campos, R. P., Vicente‐ co‐flowering Neotropical mangrove species, Avicennia germinans Silva, J., Freitas, L., & Varassin, I. G. (2012). Do pollination syndromes (Avicenniaceae) and Laguncularia racemosa (Combretaceae). Annals cause modularity and predict interactions in a pollination network of Botany, 111, 207–214. https://doi.org/10.1093/aob/mcs265. in tropical high‐altitude grasslands? Oikos, 121, 35–43. https://doi. Larson, B. M. H., & Barrett, S. C. H. (1999a). The pollination ecology of org/10.1111/j.1600-0706.2011.19089.x. buzz‐pollinated Rhexia virginica (Melastomataceae). American Journal De Jong, T. J., Waser, N. M., & Klinkhamer, P. G. (1993). Geitonogamy: of Botany, 86, 502–511. https://doi.org/10.2307/2656811. The neglected side of selfing. Trends in Ecology & Evolution, 8, 321– Liu, H., & Pemberton, R. W. (2009). Solitary invasive orchid bee out- 325. https://doi.org/10.1016/0169-5347(93)90239-L. performs co‐occurring native bees to promote fruit set of an inva- De Luca, P. A., Bussiere, L. F., Souto‐Vilaros, D., Goulson, D., Mason, sive Solanum. Oecologia, 159, 515–525. https://doi.org/10.1007/ A. C., & Vallejo‐Marín, M. (2013). Variability in bumblebee pol- s00442-008-1232-6. lination buzzes affects the quantity of pollen released from Luo, Z. L., Gu, L., & Zhang, D. X. (2009). Intrafloral differentiation of sta- flowers. Oecologia, 172, 805–816. https://doi.org/10.1007/ mens in heterantherous flowers. Journal of Systematics and Evolution, s00442-012-2535-1. 47, 43–56. https://doi.org/10.1111/j.1759-6831.2009.00002.x. MESQUITA‐NETO et al. Functional Ecolo gy | 11

Luo, Z., Zhang, D., & Renner, S. S. (2008). Why two kinds of stamens in Renner, S. S. (2007). Evolutionary biology: Structure in mutualistic net- buzz‐pollinated flowers? Experimental support for Darwin's division‐ works. Nature, 448, 877. https://doi.org/10.1038/448877a. of‐labour hypothesis. Functional Ecology, 22, 794–800. https://doi. Russell, A. L., Buchmann, S. L., & Papaj, D. R. (2017). How a generalist org/10.1111/j.1365-2435.2008.01444.x. bee achieves high efficiency of pollen collection on diverse floral re- Maruyama, P. K., Vizentin‐Bugoni, J., Dalsgaard, B., & Sazima, M. (2015). sources. Behavioral Ecology, 28, 991–1003. https://doi.org/10.1093/ Pollination and breeding system of Canna paniculata (Cannaceae) in beheco/arx058. a montane Atlantic rainforest: Asymmetric dependence on a her- Russell, A. L., Golden, R. E., Leonard, A. S., & Papaj, D. R. (2015). Bees mit hummingbird. Acta Botanica Brasilica, 29, 157–160. https://doi. learn preferences for plant species that offer only pollen as a reward. org/10.1590/0102-33062014abb3590. Behavioral Ecology, 27, 731–740. https://doi.org/10.1093/beheco/ Maruyama, P. K., Vizentin‐Bugoni, J., Oliveira, G. M., Oliveira, P. E., & arv213. Dalsgaard, B. (2014). Morphological and spatio‐temporal mismatches Schlindwein, C., Westerkamp, C., Carvalho, A. T., & Milet‐Pinheiro, P. shape a Neotropical Savanna plant‐hummingbird network. Biotropica, (2014). Visual signalling of nectar‐offering flowers and specific mor- 46, 740–747. https://doi.org/10.1111/btp.12170. phological traits favour robust bee pollinators in the mass‐flowering Matsumoto, T., Yasumoto, A. A., Nitta, K., Hirota, S. K., Yahara, T., & tree Handroanthus impetiginosus (Bignoniaceae). Botanical Journal Tachida, H. (2015). Difference in flowering time can initiate specia- of the Linnean Society, 176, 396–407. https://doi.org/10.1111/ tion of nocturnally flowering species. Journal of Theoretical Biology, boj.12212. 370, 61–71. https://doi.org/10.1016/j.jtbi.2015.01.036. Solís‐Montero, L., & Vallejo‐Marín, M. (2017). Does the morphological Mesquita‐Neto, J. N., Costa, B. K. P., & Schlindwein, C. (2017). Heteranthery fit between flowers and pollinators affect pollen deposition? An as a solution to the demand for pollen as food and for pollination‐ experimental test in a buzz‐pollinated species with anther dimor- Legitimate flower visitors reject flowers without feeding anthers. Plant phism. Ecology and Evolution, 7, 2706–2715. https://doi.org/10.1002/ Biology, 19, 942–950. https://doi.org/10.1111/plb.12609. ece3.2897. Mesquita‐Neto, J. N., Blüthgen, N., & Schlindwein, C. (2018). Data from: Solís‐Montero, L., Vergara, C. H., & Vallejo‐Marín, M. (2015). High inci- Flowers with poricidal anthers and their complex interaction net- dence of pollen theft in natural populations of a buzz‐pollinated plant. works—Disentangling legitimate pollinators and illegitimate visitors. ‐Plant Interactions, 9, 599–611. https://doi.org/10.1007/ Figshare. https://doi.org/10.6084/m9.figshare.6073598. s11829-015-9397-5. Michener, C. D. (1962). An interesting method 01 pollen collecting by Souza, J. M. T., Snak, C., & Varassin, I. G. (2017). Floral divergence and bees from flowers with tubular anthers. Revista De Biología Tropical, temporal pollinator partitioning in two synchronopatric species of 10, 167–175. https://doi.org/10.15517/rbt.v10i2.31044. Vigna (Leguminosae‐Papilionoideae). Arthropod‐Plant Interactions, Olesen, J. M., Bascompte, J., Dupont, Y. L., & Jordano, P. (2007). The mod- 11, 285–297. https://doi.org/10.1007/s11829-017-9498-4. ularity of pollination networks. Proceedings of the National Academy Stone, G. N., Willmer, P., & Rowe, J. A. (1998). Partitioning of pollina- of Sciences of the United States of America, 104, 19891–19896. https:// tors during flowering in an African Acacia community. Ecology, doi.org/10.1073/pnas.0706375104. 79, 2808–2827. https://doi.org/10.1890/0012-9658(1998) Olesen, J. M., Dupont, Y. L., Hagen, M., Trøjelsgaard, K., & Rasmussen, 079[2808:POPDFI]2.0.CO;2. C. (2011). Structure and dynamics of pollination networks: The past, Switzer, C. M., Hogendoorn, K., Ravi, S., & Combes, S. A. (2016). present and future. In S. Patiny (Ed.), Evolution of plant‐pollinator rela‐ Shakers and head bangers: Differences in sonication behavior be- tionships (pp. 374–391). Cambridge, UK: Cambridge University Press. tween Australian Amegilla murrayensis (blue‐banded bees) and Ollerton, J. (1996). Reconciling ecological processes with phylogenetic North American Bombus impatiens (bumblebees). Arthropod‐Plant patterns: The apparent paradox of plant‐pollinator systems. Journal Interactions, 10, 1–8. https://doi.org/10.1007/s11829-015-9407-7. of Ecology, 84, 767–769. https://doi.org/10.2307/2261338. Vallejo‐Marín, M., Da Silva, E. M., Sargent, R. D., & Barrett, S. C. Patefield, W. M. (1981). Algorithm AS 159: An efficient method of gener- (2010). Trait correlates and functional significance of heteranth- ating random R× C tables with given row and column totals. Journal ery in flowering plants. New Phytologist, 188, 418–425. https://doi. of the Royal Statistical Society. Series C (Applied Statistics), 30, 91–97. org/10.1111/j.1469-8137.2010.03430.x. https://doi.org/10.2307/2346669. Vizentin‐Bugoni, J., Maruyama, P. K., Debastiani, V. J., Duarte, L. D. S., Peel, M. C., Finlayson, B. L., & McMahon, T. A. (2007). Updated world Dalsgaard, B., & Sazima, M. (2016). Influences of sampling effort map of the Köppen‐Geiger climate classification. Hydrology and Earth on detected patterns and structuring processes of a Neotropical System Sciences Discussions, 4, 439–473. https://doi.org/10.5194/ plant–hummingbird network. Journal of Animal Ecology, 85, 262–272. hess-11-1633-2007. https://doi.org/10.1111/1365-2656.12459. Pinto, C. E., Oliveira, R., & Schlindwein, C. (2008). Do consecutive flower Vogel, S. (1981). Bestäubungskonzepte der Monokotylen und ihr visits within a crown diminish fruit set in mass‐flowering Hancornia Ausdruck im System. Plant Biology, 94, 663–675. https://doi. speciosa (Apocynaceae)? Plant Biology, 10, 408–412. https://doi. org/10.1111/j.1438-8677.1981.tb03434.x. org/10.1111/j.1438-8677.2008.00045.x. Wanigasekara, R. W. M. U. M., & Karunaratne, W. A. I. P. (2012). Queiroz, J. A., Quirino, Z. G., & Machado, I. C. (2015). Floral traits driving Efficiency of buzzing bees in fruit set and seed set of Solanum viola‐ reproductive isolation of two co‐flowering taxa that share vertebrate ceum in Sri Lanka. Psyche: A Journal of Entomology, 2012, ID 231638. pollinators. AoB Plants, 7, plv127. https://doi.org/10.1093/aobpla/ 10.1155/2012/231638. plv127. Waser, N. M. (1978a). Competition for hummingbird pollination and se- R Core Team (2017). R: A language and environment for statistical com‐ quential flowering in Colorado wild flowers. Ecology, 59, 934–944. puting. Vienna, Austria: R Foundation for Statistical Computing. https://doi.org/10.2307/1938545. Retrieved from https://www.r-project.org. Waser, N. M. (1978b). Interspecific pollen transfer and competition be- Rego, J. O., Oliveira, R., Jacobi, C. M., & Schlindwein, C. (2018). Constant tween co‐occurring plant species. Oecologia, 36, 223–236. https:// flower damage caused by a common puts survival of a doi.org/10.1007/BF00349811. threatened buzz‐pollinated species at risk. Apidologie, 49, 276–286. Waser, N. M., Chittka, L., Price, M. V., Williams, N. M., & Ollerton, J. https://doi.org/10.1007/s13592-017-0552-0. (1996). Generalization in pollination systems, and why it matters. Renner, S. S. (1983). The widespread occurrence of anther destruction Ecology, 77, 1043–1060. https://doi.org/10.2307/2265575. by Trigona bees in Melastomataceae. Biotropica, 15, 251–256. https:// Waser, N. M., & Fugate, M. L. (1986). Pollen precedence and stigma doi.org/10.2307/2387649. closure: A mechanism of competition for pollination between 12 | Functional Ecology MESQUITA‐NETO et al.

Delphinium nelsonii and Ipomopsis aggregata. Oecologia, 70, 573–577. SUPPORTING INFORMATION https://doi.org/10.1007/BF00379906. Westerkamp, C. (1997a). Flowers and bees are competitors–not part- Additional supporting information may be found online in the ners. Towards a new understanding of complexity in specialised bee Supporting Information section at the end of the article. flowers. Acta Horticulturae, 437, 71–74. https://doi.org/10.17660/ ActaHortic. 1997.437.5. Westerkamp, C. (1997b). Keel blossoms: Bee flowers with adaptations How to cite this article: Mesquita-Neto JN, Blüthgen N, against bees. Flora (Jena), 192, 125–132. https://doi.org/10.1016/ S0367-2530(17)30767-3. Schlindwein C. Flowers with poricidal anthers and their Westerkamp, C., & Claßen‐Bockhoff, R. (2007). Bilabiate flowers: The complex interaction networks—Disentangling legitimate ultimate response to bees? Annals of Botany, 100, 361–374. https:// pollinators and illegitimate visitors. Funct Ecol. 2018;00:1–12. doi.org/10.1093/aob/mcm123. https://doi.org/10.1111/1365-2435.13204 Yoshikawa, T., & Isagi, Y. (2013). Determination of temperate bird–flower interactions as entangled mutualistic and antagonistic sub‐networks: Characterization at the network and species levels. Journal of Animal Ecology, 83, 651–660. https://doi.org/10.1111/1365-2656.12161.