Abstract
Background
Most tropical and subtropical plants are biotically pollinated, and insects are the major pollinators. A small but ecologically and economically important group of plants classified in 28 orders, 67 families and about 528 species of angiosperms are pollinated by nectar-feeding bats. From a phylogenetic perspective this is a derived pollination mode involving a relatively large and energetically expensive pollinator. Here its ecological and evolutionary consequences are explored.
Scope and Conclusions
This review summarizes adaptations in bats and plants that facilitate this interaction and discusses the evolution of bat pollination from a plant phylogenetic perspective. Two families of bats contain specialized flower visitors, one in the Old World and one in the New World. Adaptation to pollination by bats has evolved independently many times from a variety of ancestral conditions, including insect-, bird- and non-volant mammal-pollination. Bat pollination predominates in very few families but is relatively common in certain angiosperm subfamilies and tribes. We propose that flower-visiting bats provide two important benefits to plants: they deposit large amounts of pollen and a variety of pollen genotypes on plant stigmas and, compared with many other pollinators, they are long-distance pollen dispersers. Bat pollination tends to occur in plants that occur in low densities and in lineages producing large flowers. In highly fragmented tropical habitats, nectar bats play an important role in maintaining the genetic continuity of plant populations and thus have considerable conservation value.
Keywords: Angiosperms, nectar-feeding bats, plant phylogeny, pollen dispersal, pollination modes
INTRODUCTION
The floral biology of angiosperms is dominated by biotic pollination, especially in the tropics where up to 99 % of species in some habitats are animal-pollinated (Bawa, 1990). Insects account for most of these interactions, and pollination by vertebrates is relatively uncommon. In a variety of lowland tropical forests, for example, pollination by birds and bats occurs in only 3–11 % of species (Devy and Davidar, 2003). Overall, bird pollination is more common than bat pollination both locally and globally and occurs in nearly 500 genera of plants; bat pollination occurs in approximately 250 genera (Sekercioglu, 2006). At least six families or subfamilies of tropical and subtropical birds are strongly adapted for nectar-feeding. By comparison, only two families of tropical bats contain flower-visitors, and morphologically specialized nectar-feeders are in the minority in both of these families (Fleming and Muchhala, 2008).
Compared with most insects, flower-visiting birds and bats are much larger, have greater energy requirements because of their endothermic metabolism, can carry larger pollen loads, are longer-lived and may be cognitively more sophisticated. Despite the potentially greater costs to plants to attract and reward these larger pollinators, the benefits of vertebrate pollination can be substantial, especially in habitats where insect activity is limited by harsh climatic conditions (e.g. on tropical mountains; Cruden, 1972). Positive aspects of vertebrate pollination include potentially more reliable visitation and the ability to carry large pollen loads considerable distances. Compared with many insects, birds and bats are excellent in promoting outcrossing, and as a result, most vertebrate-pollinated plants have hermaphroditic breeding systems; very few are dioecious (Renner and Ricklefs, 1995).
This review focuses on the evolution of bat pollination in tropical and subtropical angiosperms. This is to address two fundamental evolutionary questions: what are the causes and what are the consequences of the evolution of this pollination method? Ancillary questions include: (1) how many times during angiosperm history and in what places has bat pollination evolved? (2) What are the phylogenetic consequences of bat pollination? How many higher level taxa (genera, tribes, subfamilies, families, etc.) have evolved in association with bat pollination? And (3) by what phylogenetic routes has bat pollination evolved? How often have bat-pollinated flowers evolved from insect-, bird-, or non-volant mammal-pollinated flowers? Before examining these questions, we provide a brief overview of flower-visiting bats and the basic characteristics of bat pollination. We then examine this pollination mode from a phylogenetic and biogeographical perspective for both plants and bats. Finally, we discuss the various evolutionary routes that have resulted in bat pollination.
FLOWER-VISITING BATS
Only two of the 18 currently recognized families of bats (Simmons, 2005) contain species that are morphologically specialized for nectar-feeding. We discount the Mystacinidae, which is endemic to New Zealand and contains one genus, Mystacina, that is known to visit terrestrial flowers (Lord, 1991), as being highly evolved for flower-visiting. Insectivory is by far the most common feeding mode in bats and is undoubtedly the ancestral feeding mode in the order Chiroptera (Simmons et al., 2008). The two families that contain nectar-feeding bats (hereafter ‘nectar bats’) include Pteropodidae (Old World flying foxes and their relatives), which occurs throughout tropical and subtropical regions of Africa including Madagascar, Asia including Indonesia, Australia and Papua New Guinea, and Pacific islands, and Phyllostomidae (American leaf-nosed bats), which inhabits tropical and subtropical regions of the Americas. These two families occur in different suborders of Chiroptera (Yinpterochiroptera and Yangochiroptera for pteropodids and phyllostomids, respectively) and are only distantly related.
The Pteropodidae contains 43 genera and about 186 species (Simmons, 2005), of which only six genera and 15 species, originally grouped together in the subfamily Macroglossinae, are morphologically specialized for flower visiting (Andersen, 1912) (Appendix 1). Molecular phylogenies of bats (Jones et al., 2005; Teeling et al., 2005) suggest that this family is approximately 56 million years old and that its crown group dates from about 26–28 Ma. Its place of origin was tropical Asia (Teeling et al., 2005). Giannini and Simmons' (2005) phylogenetic hypothesis of Pteropodidae implies that frugivory is its basal feeding mode (insectivory is virtually absent in the family) and that specialized nectarivory has evolved independently three times – twice in Asia/Australasia and once relatively recently in Africa – making the Macroglossinae paraphyletic (Kirsch and La Pointe, 1997). In addition to the morphologically specialized species, many primarily frugivorous taxa (e.g. Pteropus, Cynopterus, Epomophorus) are opportunistic flower visitors and pollinators (Baker and Harris, 1957; Ayensu, 1974; Marshall, 1985; Banack, 1998; Elangovan et al., 2000; Campbell et al., 2007) (Appendix 1). The Pteropodidae is unique among bats in that its members do not use ultrasonic echolocation for communication, orientation or foraging. Examples of specialized and opportunistic nectar-feeding pteropodids are shown in Fig. 1.
Fig. 1.
Portraits of flower-visiting bats. Approximate body masses are in parentheses. (A) Glossophaga soricina (10 g), a basal glossophagine; (B) Choeronycteris mexicana (16 g), a derived glossophagine; (C) Artibeus jamaicensis (45 g) and (D) Phyllostomus elongatus (60 g), two opportunistic flower-visiting phyllostomids; (E) Syconycteris australis (20 g) and (F) Eonycteris spelaea (70 g), two specialized nectarivorous pteropodids; (G) Pteropus poliocephalus (750 g) and (H) Epomophorus gambianus (100 g), two opportunistic flower-visiting pteropodids. Photo credits: Merlin D. Tuttle, Bat Conservation International.
The New World flower-visiting counterparts of pteropodids are members of a monophyletic clade of Phyllostomidae containing the subfamilies Glossophaginae, Phyllonycterinae and Brachyphyllinae. We will call this clade ‘glossophagines’. In contrast to pteropodids, phyllostomids are echolocating bats whose ancestral feeding mode was insectivory (Ferrarezzi and Gimenez, 1996). Both nectarivory and frugivory are derived feeding modes, and echolocation is used in addition to vision and olfaction to locate food (von Helversen and von Helversen, 1999). The glossophagine clade contains 16 genera and about 38 species (Simmons, 2005) (Appendix 1). The family Phyllostomidae is younger than the Pteropodidae and dates from 39 Ma (Jones et al., 2005; Teeling et al., 2005). Glossophagines are younger still and date from about 12 Ma (Davalos, 2004). In addition to the morphologically specialized glossophagines, a number of frugivorous or omnivorous phyllostomids are opportunistic flower-visitors (Appendix 1). Examples of specialized and opportunistic nectar-feeding phyllostomids are shown in Fig. 1.
As described in detail by Freeman (1995) and others, specialized nectar bats in the two families share a common set of morphological features. These include an elongated rostrum, dentition that is reduced in size and number of teeth, and a long tongue tipped with hair-like papillae which is used to collect nectar rapidly during brief flower visits. Despite sharing these morphological characteristics, pteropodids and phyllostomids differ in several important aspects that affect their interaction with flowers. First, glossophagine bats are significantly smaller than their pteropodid counterparts. Mean glossophagine mass is about 14 g (range 7·5–30 g) compared with 38 g (range 13·2–82·2 g) in pteropodids (Fleming and Muchhala, 2008). Second, the range of rostral and tongue lengths (relative to overall size) of phyllostomids is much greater than that of pteropodids (Muchhala, 2006a; Fleming and Muchhala, 2008). The glossophagine Anoura fistulata of the northern Andes, for instance, has the longest tongue (but not the longest rostrum) relative to its body length of any mammal (Muchhala, 2006a). Third, all glossophagine bats typically hover when visiting flowers whereas specialized pteropodids always land on flowers before feeding (Fig. 2). Visits to flowers by members of both families, however, are brief and usually last <2 s (e.g. Horner et al., 1998; von Helversen and Winter, 2003; Srithongchuay et al., 2008). Opportunistic flower visitors in both families are generally larger than specialized flower visitors (up to about 1000 g in pteropodids and 50 g in phyllostomids) and land on flowers rather than hover to feed (Fig. 2). In summary, New World specialized nectar bats are smaller in size with longer tongues and hover whereas their Old World counterparts are larger with shorter tongues and do not hover. Because of these differences, we might expect plants visited by specialized nectar-feeding phyllostomids to produce smaller flowers with smaller nectar volumes per flower than those visited by their pteropodid counterparts (von Helversen, 1993).
Fig. 2.
Nectar-feeding bats visiting flowers. (A) Glossophaga soricina at flowers of Mabea occidentalis (Euphorbiaceae); (B) Artibeus jamaicensis on a flower of Ochroma pyramidale (Bombacaceae s.s.); (C) Eonycteris spelaea on flowers of Durio zibethinus (Bombacaceae s.s.); (D) Pteropus conspicillatus at flowers of Castanospermum australe (Fabaceae). Photo credits: Merlin D. Tuttle, Bat Conservation International.
The taxonomic richness of flower-visiting bats in both hemispheres varies among regions and within regions with latitude, habitat and elevation (Fleming, 1993, 1995). At the regional level, generic richness, which is used as a surrogate for morphological diversity throughout this review, in Pteropodidae is 12 (including one genus of specialized nectarivore) in Africa, 14 (two) in mainland Asia, nine (two) in Papua New Guinea, five (two) in Australia, and 21 (four) in the islands of south-east Asia and the western Pacific for a total of about 186 species (Nowak, 1994; Simmons, 2005). Generic richness in plant-visiting phyllostomids is 23 (ten specialized) in South America, 21 (11) in Mexico and Central America, and 13 (five) in the West Indies for a total of about 108 species (Nowak, 1994; Simmons, 2005). At the local or community level, species richness in pteropodids averages 2·3 specialized nectar bats (n = 4 sites; range, 1–3) whereas it averages 4·4 specialized species in phyllostomids (n = 14 sites; range, 2–6; Fleming and Muchhala, 2008). In both families, the number of species of nectar bats per habitat declines steadily with an increase in elevation and includes only one or two species above 2000 m (Heaney et al., 1989; Fleming et al., 2005).
An analysis of community trends in phyllostomid nectar bats with a comparison with their avian analogues, hummingbirds (Fleming et al., 2005), showed that (1) the highest species richness (S) in nectar bats occurs in lowland moist or wet tropical forests; (2) S increases asymptotically with rainfall with a plateau of about five species at annual rainfall levels of 2500 mm or more; (3) S in communities of both bats and hummingbirds changes seasonally as latitudinal and altitudinal migrants move into and away from particular habitats; (4) species of Glossophaga represent the ‘core’ residents in terms of abundance and year-round presence in lowland communities, and species of Anoura are ‘core’ residents in montane communities; (5) nectar bats are larger in mass and jaw length in dry habitats than in wet habitats; and (6) average jaw length in nectar bat communities is positively correlated with average corolla length of bat-pollinated flowers in that community – this implies that these bats are generalist (fine-grained) flower visitors (compared with more specialized (coarse-grained) flower feeding in hummingbirds. Reflecting this last trend, it is common to find several different species of pollen on flower-visiting phyllostomids when captured at night or when pollen on stigmas is identified (e.g. Heithaus et al., 1975; Muchhala et al., 2009). A similar community-level analysis has not been made for pteropodid nectar bats and their Old World avian counterparts [e.g. sunbirds and honeyeaters; but see Fleming and Muchhala (2008) for a global analysis of the evolution of these vertebrates]. Based on their analysis, Fleming and Muchhala (2008) advocated a ‘three-world’ view concerning the evolution of vertebrate pollinators and their food plants – the Neotropics, Africa (including Madagascar) and Asia/Australasia – rather than a simple New World/Old World dichotomy. This trichotomy is more applicable to nectar-feeding birds than it is to bats, and we will deal only with a New World/Old World comparison in this review.
A particularly important result of the Fleming et al. (2005) study and one that was extended to Old World nectarivores as well as New and Old World avian and chiropteran frugivores by Fleming (2005) was the relationship between their species richness and that of their food plants. In the New World, S of both nectar-feeding and frugivorous bats and birds is positively correlated with S of their food plants. Although the intercepts of the regression lines for these relationships differed (higher in frugivores than in nectarivores), the slopes of the two regressions were the same (about 0·38) and indicated that for both groups, the ratio of plant species to animal species is 3 : 1. That is, it takes an average of three species of flowers or fruits to support one species of vertebrate nectarivore or frugivore. Fleming (2005) interpreted this relationship to indicate that resource S controls consumer S in New World nectarivores and frugivores. Interestingly, a similar correlation does not appear to exist in communities of Old World bat and bird nectar-feeders and fruit-eaters. In neither group did the regression coefficient differ from zero, which implies that consumer diversity is not (or is less likely to be) limited by flower or fruit resource diversity. This does not imply, however, that populations of these consumers are not food-limited. A review of data bearing on this issue clearly indicates that populations of vertebrate nectarivores and frugivores throughout the tropics are often food-limited (T. H. Fleming and W. J. Kress, unpubl. res.).
Finally, species richness of bat-pollinated plants within New and Old World communities is generally similar, averaging 11·9 (range 4–33 species) in the New World and 16·8 (range 4–28) in the Old World (Fleming, 2005). The species richness values of nectar-feeding birds and their food plants are generally higher than those of bats except for Old World flowers in which, on average, bat plants slightly outnumber bird plants at the community level (Fleming, 2005).
BAT FLOWERS AND THE BASICS OF BAT POLLINATION
Bat flowers
Pollination biologists have long recognized a set of plant characteristics (syndromes) that are associated with different kinds of pollinators. The classic characteristics of bat-pollinated flowers (the ‘chiropterophilous syndrome’), as described by Faegri and van der Pijl (1979) and modified by Howe and Westley (1988), include nocturnal anthesis, drab coloration (i.e. white or green), musty smell, flowers often located on branches or tree trunks (cauliflory) or suspended on long stalks (flagelliflory), and tubular or radially symmetrical flowers, often of the ‘shaving brush’ type, that produce relatively large amounts of hexose-rich nectar. Dobat and Peikert-Holle (1985) profusely illustrate these kinds of flowers, a few of which are shown in Figs 3 and 4.
Fig. 3.
Bat-pollinated flowers, corolla or perianth length (when known), and their pollinators. (A) Agave palmeri (Asparagales: Agavaceae), corolla tube 45–60 mm, glossophagine bats; (B) Musa acuminata (Zingiberales: Musaceae), perianth 70 mm, opportunistic and specialized pteropodid bats; (C) Heliconia solomonensis (Zingiberales: Heliconiaceae), perianth 45–75 mm, specialized pteropodid bats; (D) Canna liliiflora (Zingiberales: Cannaceae), glossophagine bats; (E) Vriesia sp. (Poales: Bromeliaceae), glossophagine bats; (F) Psittacanthus acinarius (Santalales: Loranthaceae), corolla 50–75 mm, glossophagine bats; (G) Calyptrogyne ghiesbreghtiana (Arecales: Arecaceae), rachilla 220 mm, opportunistic phyllostomid bats; (H) Phenakospermum guyannense (Zingiberales: Strelitziaceae), perianth up to 280 mm, opportunistic phyllostomid bats. Photo credits: T. Fleming (A), W. J. Kress (B–E, G, H), C. Geiselman (F).
Fig. 4.
Bat-pollinated flowers, their corolla or perianth length (when known), and their pollinators. (A) Carnegiea gigantea (Caryophyllales: Cactaceae), corolla 112 mm, opportunistic and specialized phyllostomid bats; (B) Markhamia stipulata (Lamiales: Bignoniaceae), specialized pteropodid bats; (C) Burmeistera ceratocarpa (Asterales: Campanulaceae), corolla 13·2 mm, glossophagine bats; (D) Chelonanthus alatus (Gentianales: Gentianaceae), corolla 30–45 mm, glossophagine bats; (E) Lecythis poiteaui (Ericales: Lecythidaceae), androecium 50 mm, glossophagine bats; (F) Hymenaea courbaril (Fabales: Fabaceae), flower diameter 25 mm, opportunistic and specialized phyllostomid bats; (G) Ceiba pentandra (Malvales: Malvaceae), flower diameter 25–35 mm, opportunistic and specialized phyllostomids and pteropodids; (H) Caryocar glabrum (Malpighiales: Caryocaraceae), flower diameter 40 mm, opportunistic and specialized phyllostomid bats. Photo credits: T. Fleming (A, B), C. Geiselman (D), S. Mori (E–H), N. Muchhala (C).
Knowledge of the characteristics of bat flowers has increased substantially since the review by Faegri and van der Pijl (1979), and we now know that such traits as flower colour are far more variable among bat-pollinated flowers than previously thought (Figs 3 and 4). It remains true, however, that bat flowers occupy a distinct subset of multivariate floral morphological space compared with flowers pollinated by other kinds of animals (Ollerton et al., 2009). Bats, like many other kinds of pollinators, can be opportunistic flower visitors and sometimes visit flowers that do not conform to the classic ‘bat pollination syndrome’ (e.g. bee flowers such as Thunbergia grandiflora, hummingbird-pollinated flowers such as Calliandra laxa, and hummingbird feeders; Lemke, 1985; T.H. Fleming, pers. obs.). Nonetheless, most kinds of flowers that they visit differ strongly from flowers visited by other kinds of pollinators. Hence, we agree with Fenster et al. (2004), among others, that the concept of pollination syndromes has considerable heuristic value and that it should be retained in the pollination literature.
Floral characteristics associated with bat pollination appear to have evolved to attract relatively large, nocturnal, colour-blind, volant pollinators. Advertising their presence with a musty, fetid odour is a common feature among bat flowers. For instance, sulphur-containing compounds, which give some bat flowers their characteristic odour, are uncommon in most floral aromas, but have been isolated multiple times from evolutionarily unrelated bat flowers in the Neotropics (Bestmann et al., 1997; von Helversen et al., 2000). The colour of bat flowers ranges from white, brown and green to pink, fuchsia and yellow (Winter and von Helversen, 2001; von Helversen and Winter, 2003). Although white or light-coloured flowers appear to stand out against foliage or the night sky (Hopkins, 1986), many bat flowers are quite dull in colour, which may function more as a camouflage from other visitors than as a visual cue to bats (Knudsen et al., 2006). Some of this variation may reflect the pollination syndrome from which bat-pollinated species evolved (e.g. red from bird-pollinated and white or yellow from moth-pollinated species; Tripp and Manos, 2008). Finally, some floral advertisements are clearly directed at echolocating bats. The best example is the virgin flower of Mucuna holtonii (Fabaceae), which offers an average of five times more nectar than one that has already been visited. These flowers indicate their status by returning echoes over an increased angle of reflectance to echolocating bats (von Helversen and von Helversen, 1999). Bats seem to associate the echoes of virgin flowers with their larger rewards and, when given a choice, were found to visit them significantly more often than opened flowers (von Helversen and Winter, 2003).
While odour, colour and echoes signal the presence of a bat flower, it is ultimately the nutritional reward, including nectar, pollen and edible plant tissues [e.g. in Freycinetia insignis (Pandanaceae) and Calyptrogyne ghiesbreghtiana (Arecaceae)], that entices bats to visit flowers (van der Pijl, 1956; Gould, 1978; Cunningham, 1995a). In many cases, bat flowers are visited for their nectar and only indirectly for pollen, which is later groomed off the fur following multiple flower visits. Certain glossophagines (e.g. Anoura geoffroyi, Leptonycteris curasoae) and the pteropodid Syconycteris australis, however, are known to consume and digest the contents of pollen grains, and it is likely that other nectar bats also have this ability (Howell, 1974; Law, 1992; Herrera and Martínez del Río, 1998). In general, chiropterophilous flowers produce more nectar than those in any other syndrome, although the amount varies greatly between species from as little as 10 µL to as much as 15 mL per flower per night (van der Pijl, 1961; Cruden et al., 1983; Winter and von Helversen, 2001). Plants pollinated by hovering glossophagines, however, can satisfy their pollinators with smaller rewards due to their pollinators' size and energetic efficiencies in flower detection and acquisition (von Helversen, 1993). In contrast to the large amount produced, most nectar from bat flowers is rather dilute with sugar concentrations ranging from 5 to 29 % (von Helversen, 1993). Both nectar amount and its sugar concentration appear to play a role in attracting or deterring bat visits to flowers (Gould, 1978; Sazima and Sazima, 1987). For example, Gottsberger and Silberbauer-Gottsberger (2006) suggested that Luehea grandiflora (Malvaceae) is visited exclusively by glossophagines in the cerrado region of Brazil not because it physically excludes opportunistic bats, but because its nectar supply may be insufficient to attract larger bats. In addition to nectar amount and concentration, energy savings associated with the ease in locating and handling conspicious flowers also factor into determining the net reward of visitation (Heinrich, 1975; Winter and von Helversen, 2001).
Olfactory and visual cues and rewards are responsible for attracting bats to flowers, but it is the flower's size, shape and durability, its placement on the plant, and time of anthesis that determine whether a bat has access to it and can affect pollination. Compared with many insect- or bird-pollinated flowers (but not hawkmoth flowers), bat-pollinated flowers are often relatively large and robust. The original bat pollination syndrome was based on plants pollinated by large, non-hovering pteropodids and applies less widely to New World plants pollinated by hovering phyllostomids (von Helversen, 1993; von Helversen and Winter, 2003). These plants tend to produce smaller and more delicately built flowers than those visited by pteropodids or opportunistic nectar-feeding phyllostomids (Figs 2–4).
Bat flowers/inflorescences can be roughly divided into three categories based on their shape: (1) ‘shaving-brush’ or ‘stamen ball’ with many projecting stamens (e.g. Bombax, Capparis, Eugenia, Parkia); (2) ‘bell-shaped’ with the corolla forming a tube (e.g. Bauhinia, Musa, Vriesea); and (3) ‘cup-shaped’ with an open corolla (e.g. Carnegiea, Caryocar, Ceiba, Ipomoea, Ochroma) (Baker, 1973; Salas, 1973; von Helversen, 1993; Figs 3 and 4). Similarly, flower shape shows different trends associated with bat visitors. Flowers visited by specialized nectar-feeding phyllostomids are more likely to be tubular in shape and produced by epiphytes and shrubs while flowers visited by pteropodids tend to be produced by trees and of the ‘shaving brush’ type (Fleming and Muchhala, 2008).
Of the five flower characteristics limiting or allowing bat access to flowers, only two appear to be universal or nearly so for all bat flowers. The first is flower/inflorescence placement away from foliage, such as projecting above or below the canopy, emerging from branches or trunk, or borne on deciduous trees after they have dropped their leaves (van der Pijl, 1941, 1956, 1961) (Figs 3 and 4). Both visually orientating and echolocating bats benefit from this arrangement as it allows them easily to find, approach and depart from flowers (von Helversen, 1993). Nocturnal anthesis, the opening of flower buds in the late afternoon or at night, is the second characteristic. The flowers of many bat-pollinated plants open early in the evening and are viable for only one night (Faegri and van der Pijl, 1979). Exceptions include flowers of Passiflora mucronata, which do not open until after midnight, and those of Burmeistera, which remain open for up to 3 d (Sazima and Sazima, 1978; Muchhala, 2006b). Together, flower placement away from foliage and nocturnal anthesis are the unifying features of the bat pollination syndrome while all other characteristics discussed above, which provide cues and incentives to entice visitation, vary among bat-pollinated species.
Whether or not they are common among all bat flowers or were selected for by bats, many floral characteristics seem to make flowers easier for bats to find as they mirror the sensory abilities of their pollinators. Both pteropodid and phyllostomid bats use a variety of sensory modes, including vision, olfaction and echolocation (phyllostomids only), to locate flowers. Both groups of plant-visiting bats have keen senses of smell and appear to use olfaction for long-distance detection of flowers (Marshall, 1983; von Helversen, 1993). Phyllostomid and pteropodid nectarivores, however, diverge in the chemical components to which they seem most attracted. In captive studies, glossophagines responded most strongly to aromas dominated by dimethyl sulphides while the pteropodid Cynopterus sphinx appeared to be more attracted to aromas containing ethyl acetate (von Helversen et al., 2000; Elangovan et al., 2006).
Members of these two families of bats rely on their vision to navigate, communicate with roostmates, detect predators and locate food (Suthers, 1970). Pteropodids, which lack the ability to echolocate (except crudely in Rousettus), depend entirely on vision to negotiate their environment and appear to do so quite well even in inclement weather and on moonless nights (Gould, 1978). Visually orientating bats seem capable of discerning white flowers against the dark backdrop of foliage or the night sky (Winter and von Helversen, 2001). Some species of glossophagines appear to recognize patterns, and Glossophaga soricina has been shown to detect ultraviolet radiation, which may enable it to locate ultraviolet-reflecting flowers (Suthers, 1970; Winter and von Helversen, 2001; Winter et al., 2003). In addition to sight, nectar-feeding phyllostomids use ‘whispering’ (low-intensity) echolocation that allows them to navigate in cluttered environments where many of their food plants occur (Winter and von Helversen, 2001). Both flower-visiting pteropodids and phyllostomids undoubtedly rely on their excellent spatial memories to relocate plants they have visited previously, although this ability has only been examined experimentally in glossophagines (Winter and Stich, 2005). This ability probably allows them to minimize search costs, especially when feeding on plants with extended, or ‘steady-state’ (sensu Gentry, 1974), blooming periods (Tschapka and von Helversen, 2007).
Bat roosting and foraging
The roosting and foraging behavior of nectar-feeding bats can affect their interactions with plants and flowers in a variety of ways. Because they lack the ability to echolocate, most pteropodids roost either gregariously in the foliage of canopy trees or solitarily in understorey vegetation rather than in dark caves. Two exceptions are the specialized nectar bat Eonycteris spelaea, which roosts in caves in colonies of a few dozen to thousands of individuals in Malaysia (Start and Marshall, 1976), and Notopteris macdonaldi of New Caledonia, the Hebrides and Fiji, which forms small colonies in caves. Gregarious bats, including canopy-roosting species of Pteropus and Eidolon which sometimes live in colonies of hundreds of thousands of bats, and cave-roosting species such as Eonycteris forage as much as 50 km away from their day roosts and are potentially long-distance pollen carriers (Gould, 1978; Marshall, 1985). Solitary roosting pteropodids, such as species of Syconycteris and Macroglossus in Australasia, forage much closer (i.e. hundreds of metres to a few kilometres) to their day roosts and hence are likely to be shorter-distance pollen carriers (Law, 1993; Law and Lean, 1999).
Territorial feeding behaviour, which can strongly limit the distance that pollen moves (e.g. in territorial hummingbirds; Linhart, 1973; Linhart et al., 1987), is known to occur in both gregarious and solitary pteropodids. For example, adult males of Syconycteris australis defend feeding territories against juvenile males and females when feeding at Banksia flowers in south-eastern Australia (Law, 1996); this probably results in sex- and age-biased pollen movement patterns in this species, but data to support this suggestion are not yet available. Males of Macroglossus minimus and Melonycteris melanops are thought to defend resource plants against other males (Winkelmann et al., 2003; Bonaccorso et al., 2005). More dramatically, adults of various species of Pteropus in Australia and elsewhere set up small feeding territories in the canopies of flowering (and fruiting) trees which they defend against socially subordinate, usually younger, individuals. If allowed to visit flowers, subordinates are more likely to move pollen (and seeds) further away from parent plants than the territory-holders (Richards, 1995; McConkey and Drake, 2006).
In contrast to pteropodids, most flower-visiting phyllostomids roost in relatively small colonies of a few dozen to hundreds of individuals in caves. An exception to this is the migratory bat Leptonycteris curasoae (= yerbabuenae), which lives in large colonies of tens of thousands of individuals in arid and semi-arid parts of Mexico and south-western Arizona. The foraging radius of these colonies can be 30–50 km, and these bats are excellent long-distance pollen movers (Horner et al., 1998; Fleming, 2004). Also in contrast to pteropodids, territorial defence of flowers appears to be uncommon in phyllostomid bats. Instead, like hermit hummingbirds, many species are thought to be trap-liners that each night visit a series of widely spaced flowers, often in the canopy of wet tropical forests (Baker, 1973; Heithaus et al., 1974; Lemke, 1984; Tschapka, 2004). Together, their spatial memory and trapline foraging behaviour enable glossophagines to exploit floral resources that have temporally dynamic availability in spatially predictable feeding sites (Baker, 1973; Gould, 1978; Fleming, 1982; Lemke, 1984, 1985; von Helversen, 1993; Winter and von Helversen, 2001). This behaviour probably results in substantial pollen movement among plants. For instance, Dick et al. (2008) reported that pollen moved about 18 km between individuals in the bat-pollinated Ceiba pentandra in Brazilian riverine forest habitat. Among arid-zone columnar cacti, between-population genetic structure, as indicated by Wright's Fst index, is lower in bat-pollinated taxa than in insect-pollinated taxa, which implies that bat-mediated gene flow is greater than that mediated by insects (Hamrick et al., 2002). Similarly, low levels of genetic subdivision occur in Phenakospermum guyannenase (Strelitziaceae), a widespread bat-pollinated Amazonian megaherb (Roesel et al., 1996).
PHYLOGENETIC AND GEOGRAPHICAL DISTRIBUTIONS OF BAT POLLINATION
Phylogenetic distributions
In their review of vertebrate pollination, Fleming and Muchhala (2008, based on data in Dobat and Peikert-Holle, 1985) reported that bat pollination occurs in 58 families of plants in about 24 orders; 43 families contain flowers visited by phyllostomids and 28 by pteropodids. Thirteen of the 58 plant families (28 %) are visited by both families of bats. A more complete update of this earlier report (Geiselman et al., 2004, and onwards) indicates that phyllostomids visit 360 species of plants in 159 genera from 44 families; our literature review indicates that pteropodids visit 168 species of plants in 100 genera from 41 families. In total, bat-pollinated plants are found in 67 families in 28 orders of angiosperms (Table 1). Of these families, 26 are exclusively visited by phyllostomids and 23 are exclusively visited by pteropodids; 18 families are visited by both families of bats. Lists of known bat-pollinated species, by family, in the New and Old World are provided in Appendices 2 and 3. In compiling these lists we have attempted to include only those taxa known or strongly suspected to be pollinated by bats. As is the case in much of the pollination literature, however, actual proof of effective pollination by bats is available for only a subset of these taxa.
Table 1.
Summary of families of angiosperms known to produce flowers visited by New World (NW) and Old World (OW) bats
| Lineage | Order | Family | Distribution | Total genera | Total species | NW genera | NW spp | OW genera | OW spp. | Total bat genera | Proportion total genera |
|---|---|---|---|---|---|---|---|---|---|---|---|
| Basal angiosperms | Laurales | Lauraceae | Pantropical | 50 | 2500 | 0 | 0 | 1 | 1 | 1 | 0·020 |
| Magnoliales | Annonaceae | Pantropical | 129 | 2220 | 0 | 0 | 1 | 1 | 1 | 0·008 | |
| Monocots | Arecales | Arecaceae | Pantropical | 189 | 2361 | 3 | 3 | 4 | 4 | 7 | 0·037 |
| Asparagales | Agavaceae | Pantropical | 23 | 637 | 3 | 17 | 0 | 0 | 3 | 0·130 | |
| Amaryllidaceae | Pantropical | 11 | 146 | 2 | 2 | 0 | 0 | 2 | 0·182 | ||
| Asphodelaceae | Paleotropical | 15 | 785 | 0 | 0 | 1 | 1 | 1 | 0·067 | ||
| Asteliaceae | Southern Hemisphere | 4 | 36 | 0 | 0 | 1 | 1 | 1 | 0·250 | ||
| Xanthorrhoeaceae | Austral | 1 | 30 | 0 | 0 | 1 | 1 | 1 | 1·000 | ||
| Pandanales | Pandanaceae | Paleotropical | 4 | 885 | 0 | 0 | 2 | 4 | 2 | 0·500 | |
| Velloziaceae | Pantropical | 9 | 240 | 1 | 1 | 0 | 0 | 1 | 0·111 | ||
| Poales | Bromeliaceae | Neotropical | 57 | 1400 | 6 | 21 | 0 | 0 | 6 | 0·105 | |
| Zingiberales | Cannaceae | Neotropical | 1 | 19 | 1 | 1 | 0 | 0 | 1 | 1·000 | |
| Heliconiaceae | Neotropical + Pacific | 1 | 150 | 0 | 0 | 1 | 3 | 1 | 1·000 | ||
| Musaceae | Paleotropical | 2 | 35 | 0 | 0 | 2 | 8 | 2 | 1·000 | ||
| Strelitziaceae | Pantropical | 3 | 7 | 1 | 1 | 0 | 0 | 1 | 0·333 | ||
| Basal eudicot | Caryophyllales | Cactaceae | Neotropical | 111 | 1500 | 26 | 43 | 0 | 0 | 26 | 0·234 |
| Nyctaginaceae | Pantropical | 30 | 395 | 2 | 2 | 0 | 0 | 2 | 0·067 | ||
| Proteales | Proteaceae | Pantropical | 80 | 1600 | 1 | 1 | 3 | 7 | 4 | 0·050 | |
| Santalales | Loranthaceae | Pantropical | 68 | 950 | 1 | 1 | 2 | 2 | 3 | 0·044 | |
| Rosid | Brassicales | Capparaceae | Pantropical | 16 | 480 | 3 | 8 | 0 | 0 | 3 | 0·188 |
| Salvadoraceae | Paleotropical | 3 | 11 | 0 | 0 | 1 | 1 | 1 | 0·333 | ||
| Celastrales | Celastraceae | Cosmopolitan | 89 | 1300 | 0 | 0 | 1 | 1 | 1 | 0·011 | |
| Cucurbitales | Cucurbitaceae | Pantropical | 118 | 845 | 4 | 5 | 0 | 0 | 4 | 0·034 | |
| Fabales | Fabaceae | Cosmopolitan | 730 | 19400 | 22 | 59 | 11 | 26 | 29 | 0·040 | |
| Geraniales | Geraniaceae | Cosmopolitan | 7 | 805 | 1 | 1 | 0 | 0 | 1 | 0·143 | |
| Malpighiales | Caryocaraceae | Neotropical | 2 | 21 | 1 | 5 | 0 | 0 | 1 | 0·500 | |
| Chrysobalanaceae | Pantropical | 17 | 460 | 2 | 3 | 1 | 3 | 3 | 0·176 | ||
| Clusiaceae | Cosmopolitan | 27 | 1050 | 0 | 0 | 1 | 1 | 1 | 0·037 | ||
| Euphorbiaceae | Cosmopolitan | 218 | 5735 | 3 | 3 | 2 | 2 | 5 | 0·023 | ||
| Passifloraceae | Pantropical | 16 | 705 | 1 | 5 | 0 | 0 | 1 | 0·063 | ||
| Rhizophoraceae | Pantropical | 16 | 149 | 0 | 0 | 1 | 1 | 1 | 0·063 | ||
| Salicaceae | Cosmopolitan | 55 | 1010 | 1 | 1 | 1 | 1 | 2 | 0·036 | ||
| Malvales | Malvaceae | Cosmopolitan | 243 | 4225 | 18 | 41 | 7 | 16 | 24 | 0·099 | |
| Myrtales | Combretaceae | Pantropical | 14 | 500 | 1 | 1 | 1 | 1 | 2 | 0·143 | |
| Lythraceae | Cosmopolitan | 31 | 620 | 1 | 7 | 2 | 4 | 3 | 0·097 | ||
| Melastomataceae | Pantropical | 182 | 4570 | 2 | 2 | 0 | 0 | 2 | 0·011 | ||
| Myrtaceae | Pantropical | 131 | 4620 | 0 | 0 | 8 | 27 | 8 | 0·061 | ||
| Onagraceae | Cosmopolitan | 22 | 656 | 1 | 1 | 0 | 0 | 1 | 0·045 | ||
| Vochysiaceae | Neotropical, African | 7 | 190 | 1 | 1 | 0 | 0 | 1 | 0·143 | ||
| Oxalidales | Elaeocarpaceae | Pantropical | 12 | 605 | 0 | 0 | 1 | 3 | 1 | 0·083 | |
| Rosales | Moraceae | Pantropical | 38 | 1100 | 0 | 0 | 1 | 1 | 1 | 0·026 | |
| Rhamnaceae | Cosmopolitan | 52 | 925 | 0 | 0 | 1 | 1 | 1 | 0·019 | ||
| Rosaceae | Cosmopolitan | 90 | 2520 | 0 | 0 | 1 | 1 | 1 | 0·011 | ||
| Sapindales | Anacardiaceae | Pantropical | 70 | 600 | 0 | 0 | 1 | 1 | 1 | 0·014 | |
| Meliaceae | Pantropical | 52 | 621 | 0 | 0 | 2 | 2 | 2 | 0·038 | ||
| Sapindaceae | Pantropical | 135 | 1580 | 1 | 1 | 2 | 2 | 3 | 0·022 | ||
| Asterid | Apiales | Araliaceae | Pantropical | 43 | 1450 | 0 | 0 | 1 | 1 | 1 | 0·023 |
| Asterales | Asteraceae | Cosmopolitan | 1620 | 23600 | 3 | 3 | 0 | 0 | 3 | 0·002 | |
| Campanulaceae | Cosmopolitan | 84 | 2380 | 3 | 20 | 1 | 1 | 4 | 0·048 | ||
| Ericales | Ericaceae | Cosmopolitan | 126 | 3995 | 1 | 1 | 0 | 0 | 1 | 0·008 | |
| Lecythidaceae | Pantropical | 25 | 310 | 1 | 3 | 5 | 5 | 6 | 0·240 | ||
| Marcgraviaceae | Neotropical | 7 | 130 | 3 | 17 | 0 | 0 | 3 | 0·429 | ||
| Polemoniaceae | NW + Eurasia | 18 | 385 | 1 | 4 | 0 | 0 | 1 | 0·056 | ||
| Sapotaceae | Pantropical | 53 | 1100 | 0 | 0 | 7 | 13 | 7 | 0·132 | ||
| Gentianales | Apocynaceae | Pantropical | 415 | 4555 | 0 | 0 | 3 | 3 | 3 | 0·007 | |
| Gentianaceae | Cosmopolitan | 87 | 1655 | 4 | 8 | 0 | 0 | 4 | 0·046 | ||
| Loganiaceae | Pantropical | 13 | 420 | 0 | 0 | 1 | 1 | 1 | 0·077 | ||
| Rubiaceae | Cosmopolitan | 660 | 11150 | 3 | 3 | 3 | 3 | 6 | 0·009 | ||
| Lamiales | Acanthaceae | Pantropical | 229 | 3500 | 4 | 7 | 1 | 1 | 5 | 0·022 | |
| Bignoniaceae | Pantropical | 110 | 800 | 6 | 14 | 10 | 10 | 16 | 0·146 | ||
| Gesneriaceae | Pantropical | 147 | 3200 | 6 | 20 | 0 | 0 | 6 | 0·041 | ||
| Lamiaceae | Cosmopolitan | 236 | 7173 | 2 | 2 | 0 | 0 | 2 | 0·008 | ||
| Scrophulariaceae | Cosmopolitan | 65 | 1700 | 1 | 1 | 0 | 0 | 1 | 0·015 | ||
| Verbenaceae | Pantropical | 34 | 1175 | 2 | 2 | 0 | 0 | 2 | 0·059 | ||
| Solanales | Convolvulaceae | Cosmopolitan | 57 | 1625 | 1 | 4 | 2 | 2 | 3 | 0·053 | |
| Solanaceae | Cosmopolitan | 102 | 2460 | 7 | 13 | 1 | 1 | 8 | 0·078 | ||
| Boraginaceae | Cosmopolitan | 148 | 2740 | 1 | 2 | 0 | 0 | 1 | 0·007 | ||
| TOTAL | 159 | 360 | 100 | 168 |
For each family the data include: (1) distribution by major plant lineage and order; (2) geographical distribution; (3) total number of genera and species; (4) number of genera and species pollinated by NW or OW bats; and (5) total number of bat-pollinated genera and proportion of total genera per family that are bat-pollinated. Also indicated in bold type are families that occur on islands that contain bat-pollinated genera and species. Sources of data: major angiosperm lineages from Soltis et al. (2005); the basic list of families and number of New World bat-pollinated genera and species from Geiselman et al. (2004 and onwards); the basic list of families and number of Old World bat-pollinated genera and species comes from numerous literature sources available upon request from the authors; total number of genera and species per family from APG II (2002 and onwards); island bat families from Silva Taboada (1979), Mickleburgh et al. (1992), Gannon et al. (2005) and Marten-Rodriguez et al. (2009).
To examine the evolution of bat pollination from a plant phylogenetic perspective, we mapped 66 of the 67 plant families in Table 1 on a phylogeny organized according to now widely accepted angiosperm relationships (Soltis et al., 2005: appendix; T. H. Fleming and W. F. Kress, unpubl. res.). Only Capparaceae is missing from this phylogeny. For ease of analysis we divided the angiosperm plant families into five major groups, namely basal angiosperms, monocots, basal eudicots, rosids and asterids (Soltis et al., 2005). As van der Pijl (1961) and others have noted, bat pollination is most common in advanced lineages of angiosperms, i.e. in advanced monocots and in the rosids (Fig. 5). Our analysis shows that the distribution of bat-pollinated species at the family level (hereafter referred to simply as ‘bat families’) is distinctly uneven among the five groups and varies from 6–7 % of all families in basal angiosperms and basal eudicots to 17–22 % in monocots, rosids and asterids. The average number of genera of bat-pollinated plants per family also varies in these groups (although the differences are not quite statistically significant), but in a different pattern. Few families in the basal eudicots contain bat-pollinated taxa, but in those families where bat-pollination occurs, it is relatively common. The mean number of bat-pollinated genera per family (median, 1 s.d.) are: basal angiosperms, 1·0 (1·0, 0); monocots, 2·3 (1·0, 2·2); basal eudicots, 8·3 (3·5, 10·5); rosids, 3·9 (1·0, 7·1); and asterids, 3·9 (3·0, 3·4) (Kruskal–Wallis ANOVA based on medians, W = 8·99, d.f. = 4, P = 0·061). Families with the highest number of bat-pollinated genera include Fabaceae (30 genera, rosids), Cactaceae (24, basal eudicots), Malvaceae (25, rosids) and Bignoniaceae (15, asterids). The number of bat-pollinated genera in two of the three largest groups of angiosperms is correlated with the number of genera per family. Significant positive correlations occur in rosids (y = –038 + 0·045x, P < 0·01) and monocots (y = 1·45 + 0·035x, P < 0·01), but not in asterids, even after the Asteraceae is removed from the analysis (because of its exceptionally large number of genera) (y = 3·52 + 0·003x, P > 0·50). Regression coefficients (slopes) were similar in rosids and monocots (about 0·040), and their reciprocal values indicate that about one in every 25 genera in those groups contains a bat-pollinated species.
Fig. 5.
Cladogram showing the evolutionary relationships of orders of angiosperms and the distribution of families containing bat-pollinated taxa among them. Five types of bat pollination are highlighted: pollination only by New World phyllostomids, pollination only by Old World pteropodids, pollination by both bat families, and single species pollinated either by New World or Old World bats. Cladogram based on Soltis et al. (2005).
The proportion of total genera in a family that contains one or more bat-pollinated species varied substantially among the 67 families (Table 1). On average, 15 % (range 0·2–100 %) of genera in these families contained bat-pollinated species, and the average varied significantly among the five major groups (Kruskal–Wallis ANOVA based on medians, W = 20·28, d.f. = 4, P < 0·001): basal angiosperms, 1·4 % (median 1·4 %, 1 s.d. 0·8 %); monocots, 44·1 % (25·0 %, 40·6 %); basal eudicots, 9·4 % (5·9 %, 8·2 %); rosids, 9·1 % (4·7 %, 11·0 %) and asterids, 6·4 % (4·6 %, 7·7 %). Ten of the 67 plant families had at least 25 % of their genera with one or more bat-pollinated species. These families were concentrated in the monocots, in which seven of 13 families (54 %) contained relatively high proportions of bat-pollinated genera. All of these families are small and contain a total of seven or fewer genera (Table 1).
To take into account any phylogenetic bias in these analyses, we mapped the occurrence of bat pollination by order and family within each of the five major groups using Mesquite (version 2.0; Maddison and Maddison, 2007). The number of independent origins of bat pollination in each group at the ordinal and family levels was analysed with the character analysis by parsimony module. By ‘independent origin’ we mean that the sister-taxon of a bat-pollinated family contained no bat-pollinated species. The converse of ‘independent origin’ (i.e. non-independent origin) reflects phylogenetic clustering, or the tendency of related groups to contain bat-pollinated taxa. At the ordinal level, bat pollination has originated independently in about half of the orders in which it occurs (14 of 28 orders; Table 2, Fig. 5). At the family level, bat pollination has originated independently in about 77 % of the families in which it occurs (i.e. 51 of 66 families; Table 2).
Table 2.
Overall distribution of bat pollination among five major lineages of angiosperms by order and family
| Orders |
Families |
|||||
|---|---|---|---|---|---|---|
| Lineage | Total | No. with bat-pollinated families | No. of independent origins (%) | Total | No. with bat-pollinated genera | No. of independent origins (%) |
| Basal angiosperms | 9 | 2 | 1 (50) | 28 | 2 | 2 (100) |
| Monocots | 12 | 5 | 2 (40) | 76 | 13 | 9 (69) |
| Basal eudicots | 10 | 3 | 3 (100) | 63 | 4 | 4 (100) |
| Rosids | 14 | 12 | 5 (42) | 122 | 26 | 22 (85) |
| Asterids | 10 | 6 | 3 (50) | 104 | 21 | 14 (67) |
| Totals | 55 | 28 | 14 (50) | 393 | 66 | 51 (77) |
Also indicated are the estimated number of independent origins of bat pollination within these lineages by order and family. The phylogenetic hypothesis upon which this summary is based comes from T. H. Fleming and W. J. Kress (unpubl. res.). The number of families recognized in this hypothesis and in Table 1 differ slightly because it does not include Capparaceae.
The distribution of bat-pollinated taxa visited by phyllostomids and pteropodids differs at both the ordinal and the family level. Of the 28 orders containing bat families, only eight (29 %) contain taxa pollinated by both groups of bats (Table 1, Fig. 5). These orders include Arecales and Zingiberales (monocots); Santalales (basal eudicots); Fabales, Malvales and Myrtales (rosids); and Ericales and Gentianales (asterids). Similarly, as indicated above, only 18 of 67 families (27 %) with bat-pollinated taxa have representatives in both hemispheres. We estimate that bat pollination has evolved independently in about 85 % of these families (Table 3) and is clustered in three families of the Myrtales (Combretaceae, Lythraceae and Onagraceae), although phyllostomid bats are generally minor pollinators in these families (Table 1). Overall, pteropodid and phyllostomid bats basically interact with different orders and families of plants. Rather than being constrained at deep phylogenetic levels such as orders, these interactions have evolved independently many times in different Old and New World plant lineages.
Table 3.
Distribution of bat pollination among orders and families of angiosperms by bat family with an estimate of the number of independent origins within plant families
| Pteropodids |
Phyllostomids |
|||
|---|---|---|---|---|
| Lineage | No. of orders | No. of families (% independent) | No. of orders | No. of families (% independent) |
| Basal angiosperms | 2 | 2 (100) | 0 | 0 |
| Monocots | 3 | 8 (63) | 4 | 7 (100) |
| Basal eudicots | 2 | 2 (100) | 2 | 3 (100) |
| Rosids | 7 | 19 (90) | 8 | 16 (81) |
| Asterids | 3 | 10 (80) | 5 | 16 (81) |
| Totals | 17 | 41 (83) | 19 | 42 (86) |
This analysis is based on phylogenetic data in T. H. Fleming and W. J. Kress (unpubl. res.), which includes 66 of 67 families in Table 1.
Within each hemisphere bat-pollinated genera can be further subdivided into those visited by specialized or opportunistic nectar-feeding bats. A majority of the 159 genera with bat-pollinated species in the New World have been reported to be visited only by specialized nectar-feeding bats. Species in only 20 genera (13 %) have been reported to be visited by opportunistic nectar-feeding phyllostomids. These genera are found in eight families in seven orders and occur in monocots (Arecales, Zingiberales), basal eudicots (Caryophyllales) and asterids (Lamiales); over half of these genera are rosids (Fabales, Malpighiales, Malvales). Opportunistic nectarivores, which land on flowers, are thought to be the main pollinators of species in only four (2·5 %) of these genera (Calyptrogyne ghiesbreghtiana, Ochroma pyramidale, Parkia spp. and Phenakospermum guyannense). In contrast, in the Old World only species in eight genera (8 %) from six families (Heliconiaceae, Musaceae, Lythraceae, Myrtaceae, Moraceae and Bignoniaceae) have been reported to be visited solely by specialized nectarivorous bats. These are found among monocots (Zingiberales), rosids (Myrtales, Rosales) and asterids (Lamiales). The remaining 92 genera are visited either by both specialized and opportunistic nectar bats or only by opportunistic nectarivores. Thus, New World bat plants have evolved primarily with specialized nectar feeders whereas Old World bat plants have evolved mostly with opportunistic nectarivores.
It is important to note that analyses conducted at the ordinal and family levels are very ‘coarse’ and should not be interpreted to imply that bat pollination is ancestral in any order or family of angiosperms. As discussed below, the most insightful level of independence in the evolution of bat pollination is at the generic or species level. Bat pollination has seldom evolved at the tribal, subfamily or family level. Phylogenetic clustering (non-independence) at the ordinal and family levels simply indicates that bat pollination shows a tendency to occur in related higher-level taxa. The fact that bat pollination has rarely evolved at higher taxonomic levels (see below) emphasizes the relative recency of this mode of pollination.
Biogeographical, elevational and habitat distributions
Fifty-three of the 67 bat-pollinated families (79 %) are either pantropical or cosmopolitan in distribution (Table 1). Seven of the remaining 14 families are endemic to the Neotropics and three are endemic to the Paleotropics. Of the 26 ‘exclusive’ phyllostomid families, 19 (73 %) have pantropical or cosmopolitan distributions, and the other seven are New World endemics. Similarly, 17 of 23 ‘exclusive’ pteropodid families (74 %) have pantropical or cosmopolitan distributions, and the other six are Old World endemics. Thus, 36 of the 53 broadly distributed plant families that contain bat-pollinated plants (68 %) are pollinated by bats in only one hemisphere whereas only about one-third of them have bat-pollinated species in both hemispheres. This again emphasizes the phylogenetically independent nature of the evolution of bat pollination.
In general, bat pollination is primarily a lowland phenomenon. Very few nectar bats and their food plants occur at elevations above 2000 m. The distribution of bat-pollinated species of the Bromeliaceae, an endemic New World plant family, clearly illustrates this trend. Most bat-pollinated epiphytic bromeliads occur in wet lowland forests in Bolivia and elsewhere in the Neotropics whereas those pollinated by hummingbirds occur at mid- to high elevations; insect-pollinated species occur most frequently in warm, dry regions (Kessler and Krömer, 2000; Tschapka and von Helversen, 2007). Whereas most pteropodid nectar bats and their flowers occur in moist or wet forest habitats, glossophagine nectar bats and their flowers occur in arid as well as in moist and wet habitats. Up to six species of glossophagines, for example, can be found in the tropical dry forests of south-central Mexico (Santos and Arita, 2002), and the morphologically most specialized glossophagines in terms of rostral length and tooth reduction occur in cactus-dominated habitats in the Neotropics (Fleming, 1995; Fleming et al., 2005). Neotropical semi-arid and arid lands are especially rich in bat-pollinated species of Agavaceae, Cactaceae, Fabaceae and Malvaceae (Bombacoideae). No such association between nectar bats and arid habitats occurs in the Old World, although opportunistic Australasian pteropodid flower visitors (e.g. Pteropus spp.) are more common in dry eucalypt forests than in wet forests (Richards, 1995; Palmer et al., 2000).
Pteropodid and phyllostomid bats differ fundamentally regarding their occurrence on islands. About 62 % of pteropodid species are island-dwellers whereas only about 12 % of phyllostomid species, including five species of nectar bats in the West Indian endemic subfamily Phyllonycterinae, are restricted to islands (Fleming, 1993; Fleming et al., 2005). Pteropodids are widely distributed on islands throughout the Old World tropics as far east as the Cook Islands in the Pacific where they often act as ‘keystone’ pollinators and seed dispersers (Cox et al., 1991; Rainey et al., 1995; Banack, 1998). As expected given their wider distribution among islands, island-dwelling pteropodids interact as pollinators with a greater number of plant families than phyllostomids. Pteropodids on islands visit flowers in 21 of 41 (53 %) Old World bat-pollinated families whereas phyllostomids on islands visit flowers in only eight of 44 (18 %) New World bat-pollinated families (Table 1). Plant families pollinated by island pteropodids are concentrated in the rosids; those pollinated by phyllostomids are evenly distributed among monocots, rosids and asterids. About 90 % of these families have pantropical or cosmopolitan distributions. Families with restricted geographical distributions include Cactaceae in the New World and Musaceae and Pandanaceae in the Old World. Most of the flowers visited by bats of both families on islands are produced by trees or tree-like herbs or succulents (e.g. Heliconia and Musa in south-east Asian islands, Cactaceae in the West Indies). Exceptions include bat-pollinated species of Gesneria in the West Indies and three species of Marcgravia lianas on Dominica (Zusi and Hamas, 2001; Marten-Rodriguez and Fenster, 2008; Marten-Rodriguez et al., 2009). The predominance of bat-pollinated trees on islands is similar to the mainland situation in the Old World but contrasts with that in the Neotropical mainland where glossophagine bats pollinate many flowers produced by vines and epiphytes as well as trees (Fleming and Muchhala, 2008).
THE PHYLOGENETIC CONSEQUENCES OF BAT POLLINATION
The evolution of bat pollination has made a modest contribution to the overall species and generic diversity of angiosperms. What contribution has bat pollination made at higher taxonomic levels? How many tribes, subfamilies and families are exclusively bat-pollinated, or nearly so? Table 4 summarizes the higher order plant taxa that are associated primarily with bats for pollination. This information is presented at two taxonomic levels, at the family level and within families (i.e. subfamilies or tribes). Among families that are strongly associated with bat pollination, we include two families that have recently been reclassified into larger related families by Angiosperm Phylogeny Group (APG) II: Bombacaceae sensu stricto (s.s.; now part of Malvaceae) and Sonneratiaceae s.s. (now part of Lythraceae). We do this because current literature still uses these family names, and not all recent treatments of angiosperm phylogeny (e.g. Heywood et al., 2007) have accepted these reclassifications.
Table 4.
Higher order plant taxa that are associated primarily with bats for pollination
| (A) Families strongly associated with pollinating bats | ||
|---|---|---|
| Family | No. of genera/species in family or subfamily | Estimated age of family |
| Bombacaceae* | 16/120 | 69–65 Ma |
| Caryocaraceae | 2/25 | 111–100 Ma |
| Musaceae* | 2/35 | Stem = 87 Ma; crown = 61 Ma |
| Sonneratiaceae | 2/8 | 57 Ma |
| (B) Families with subfamilies or tribes strongly associated with pollinating bats | ||
|---|---|---|
| Family and subfamily or tribe | No. of genera/species in family | Estimated age of family |
| Agavaceae: Agavoideae | 23/637 – family | Crown = 13 Ma |
| Bignoniaceae: 2 of 7 tribes | 110/800 – family | 49·5 Ma |
| Cactaceae: Cactoideae, 2+ tribes | 92/1250 – subfamily | Crown = 30 Ma |
| Campanulaceae: Lobelioideae* | 29/1200 – subfamily | 43–23 Ma |
| Fabaceae: Mimosoideae, 2 tribes* | 82/3275 – subfamily | Crown = 59–39 Ma |
| Myrtaceae: Leptospermoideae* | 131/4620 – family | Stem = 93 Ma |
| Pandanaceae: Freycinetiodeae | 4/885 – family | Crown = 51 Ma |
| Proteaceae: Grevilleoideae* | 45/855 – subfamily | Stem = 118 Ma; crown = 82 Ma |
Family characteristics include geographical distribution and number of genera/species. Plant data in columns 1 and 2 come from Mabberly (1997) or APG II. Data on estimated ages of families come from APG II, Barker et al. (2007) and Ricklefs (2006).
* Bird pollination also occurs in these taxa
Only two small families with a total of four genera (Caryocaraceae in the Neotropics and the formerly segregated Sonneratiaceae s.s. in the Paleotropics) appear to be either exclusively or primarily bat-pollinated; two others (the formerly segregated Bombacaceae s.s. and the Musaceae) contain genera or species that are primarily bat-pollinated. All four of these families contain species exclusively pollinated by specialized bats in addition to others visited by both specialized and opportunistic nectar-feeders. Another eight families contain either subfamilies or tribes whose species rely heavily on bats for pollination. Of these families, bat pollination is especially common in Agavaceae and Cactaceae in the New World and Pandanaceae in the Old World. Among the pantropical families, bat pollination is more common in the New World than in the Old World in terms of number of bat-pollinated genera in Bombacaceae s.s., Campanulaceae and Fabaceae whereas it is more common in the Old World than in the New World in Bignoniaceae and Myrtaceae (Table 1). Of the 12 families listed in Table 4, six are either exclusively bat-pollinated or biased toward bat pollination in certain subfamilies or tribes in both hemispheres. Within certain families, therefore, pteropodid and phyllostomid bats appear to have had similar effects on angiosperm diversification. At lower phylogenetic levels (e.g. genera and species), however, phyllostomid-pollinated genera and species outnumber pteropodid-pollinated taxa by factors of 1·6 and 2·1, respectively (Table 1).
The currently estimated ages of plant families or subfamilies that are strongly associated with bat pollination generally pre-date the evolution of nectar-feeding bats (Table 4). Nectar-feeding bats probably evolved in the late Oligocene and Miocene (28–12 Mya), well after most of the families in Table 4 had originated and diversified. Only the New World Agavaceae appears to be approximately coeval with the radiation of glossophagines. Particularly striking are differences in the ages of the four families that are most strongly associated with bat pollination today (Bombacaceae s.s., Caryocaraceae, Musaceae and Sonneratiaceae s.s.; Table 4A). Each of these families appears to have evolved in the Late Cretaceous or early Cenozoic, well before the evolution of specialized nectar-feeding bats. This temporal mismatch suggests that stem members of these families were not likely to be bat-pollinated.
EVOLUTIONARY PATHWAYS TO BAT POLLINATION
Bat pollination is clearly a derived condition in most angiosperm lineages. What has been the most common evolutionary route to bat pollination: from insect-, bird- or non-volant mammal-pollinated taxa? Based on the preponderance of insect pollination in angiosperms, it is reasonable to hypothesize that bat pollination evolved most often from insect pollination. If this is true, did bat-pollinated taxa evolve most frequently from diurnally or nocturnally pollinated taxa (e.g. from bee or moth flowers, respectively)? Alternatively, the most common evolutionary route may have been from diurnal bird-pollinated species (e.g. from hummingbird flowers in the New World or from sunbird or honeyeater flowers in the Old World). Finally, as suggested by Sussman and Raven (1978), bat-pollinated flowers may have evolved from flowers pollinated by non-volant mammals such as primates, at least in the Old World.
Answering these questions requires that we have well-resolved, species-level phylogenies onto which pollination systems have been mapped. For particular plant groups in certain regions, this information is available for bird-pollinated plants. For example, within Neotropical Costus (Costaceae), hummingbird pollination has evolved independently from euglossine bee pollination at least 12 times, and it has evolved several times from insect pollination in Iochroma (Solanaceae) (Kay et al., 2005; Smith et al., 2006). Although not based on well-supported phylogenies, Grant (1994) hypothesized that hummingbird pollination evolved independently numerous times from bee- or moth-pollination in 11 plant families in western North America. Compared with those for birds, the evolutionary transitions to bat pollination are less well known. The best documented cases are summarized in Table 5, but not all of these represent unequivocal results because of the absence of species-level phylogenies. All three potential ancestral pollination modes (insects, birds and non-volant mammals) are included in these examples, and generalizations about evolutionary trends are not yet possible. We suspect that bat pollination has evolved most commonly from insect pollination in the Old World [e.g. in the Fabaceae (Mimosoideae) and Myrtaceae]. Flowers pollinated by hawkmoths and beetles also appear to be ancestral to bat flowers in certain Old World taxa. Although we judge that five of the 11 New World examples in Table 5 are equivocal (i.e. the immediate ancestor of bat-pollinated taxa is not clear), there is strong evidence of the evolution of bat flowers from bee, moth and hummingbird flowers in the other six families. It is likely that bat-pollinated taxa have evolved frequently from hummingbird-pollinated taxa in certain New World families of epiphytes (e.g. Bromeliaceae, Gesneriaceae), but strong evidence for this awaits phylogenetic studies, as is the case in the Agavaceae and Cactaceae, in which hummingbird pollination is not likely to be ancestral to bat pollination.
Table 5.
Examples of the evolution of bat pollination from other pollination modes
| Family and genus | Pollination history | Source |
|---|---|---|
| (A) Old World examples | ||
| *Bombacaeae, Adansonia | Hawkmoth pollination is ancestral; bat pollination has evolved twice (once in Africa and once in Madagascar) | Baum et al. (1998) |
| *Bombacaceae, the Cullenia/Boschia/Durio clade | Vertebrate pollination is probably basal in this clade, derived from insect (beetle) pollination. Bats are major pollinators in Cullenia and Durio; bees are major pollinators in Boschia | Nyffler and Baum (2001) |
| *Fabaceae, Parkia | Pollination by nocturnal bees is ancestral; bat pollination evolved in the New World and now occurs in most species | Luckow and Hopkins (1995) |
| (B) New World examples | ||
| *Acanthaceae, Ruellia | Multiple evolutions of bat pollination from bee (most common), hummingbird, or moth (least common) pollination | Tripp and Manos (2008) |
| Agavaceae, Agave | Moth pollination is likely to be ancestral in the family; bat pollination is derived in subgenus Agave | Good-Avila et al. (2006) |
| Bromeliaceae, several genera | Bat-pollinated species probably evolved from either insect or hummingbird pollination | Endress (1994), Benzing (2000) |
| Cactaceae, tribe Pachycereeae | Bat pollination probably is ancestral among these columnar cacti, but it is ultimately derived from insect (bee) pollination | Anderson (2001), Wallace (2002) |
| *Campanulaceae, Centropogon and Burmeistera | A clade of bat-pollinated Burmeistera and Centropogon evolved from hummingbird-pollinated Centropogon | Knox et al. (2008) |
| *Gesneriaceae, Sinningia | Bat pollination evolved independently twice from hummingbird pollination | Perret et al. (2007) |
| *Gesneriaceae, Gesnerieae | Bat pollination evolved independently from hummingbird pollination at least five times | Marten-Rodriguez et al. (2009) |
| *Lecythidaceae, Lecythis | Three bat-pollinated species evolved from euglossine bee pollination | Mori and Boeke (1987), Mori et al. (2007) |
| Passifloraceae, Passiflora | Bat-pollinated P. trisecta is nested within a lowland clade of bee-pollinated species, not within an Andean hummingbird-pollinated clade | Hansen et al. (2006) |
| *Polemoniaceae, Cobaea | Three bat-pollinated species have evolved independently twice from hummingbird pollination | Prather (1999) |
| Strelitziaceae, Phenakospermum | Evolved from arboreal mammal pollination in Africa | Kress et al. (1994) |
Asterisks (*) indicate those examples in which evidence for evolutionary transitions appears to be strong; other examples are currently equivocal pending species-level phylogenies.
Although bat pollination is usually considered to be a non-reversible evolutionary specialization (Tripp and Manos, 2008), this is not always true. In one case in the primarily neotropical genus Heliconia, closely related paleotropical species are pollinated by either small pteropodid bats or by honeyeaters, but not both (Kress, 1985; Pedersen and Kress, 1999). Recent DNA-based phylogenetic work suggests that honeyeater-pollinated species are derived from the bat-pollinated species (Kress and Specht, 2005; L. P. Lagomarsino, C. D. Specht and W. J. Kress, unpubl. res.). Similarly, a hummingbird-pollinated species of Burmeistera is derived from a bat-pollinated ancestor (Knox et al., 2008). Evidence that bat pollination can give rise to more generalized pollination systems involving birds and insects as well as bats comes from studies of saguaro cacti (Carnegiea gigantea) in the Sonoran Desert and Aphelandra acanthus in the Andes of Ecuador (Fleming et al., 2001; Muchhala et al., 2009). In both of these examples, reduced abundance of bats compared with other potential pollinators is thought to have selected for a change in floral characteristics (e.g. diurnal flower presentation) that favoured non-chiropteran pollinators.
GENERAL DISCUSSION AND CONCLUSIONS
Bat pollination is relatively uncommon in angiosperms compared with bird or insect pollination, and overall, it probably represents a novel (sensu ‘new’) type of pollination mode for these plants. Bat-pollinated taxa occur in at least 67 families and about 250 genera of angiosperms, mostly in advanced evolutionary lineages, particularly in the Zingiberales in monocots and in the rosids among eudicots. The near absence of bat pollination in the basal angiosperms (only two species) is striking. This pollination mode involves relatively large (compared with most insect pollinators), energetically expensive animals that require substantial energetic rewards per flower or inflorescence for attraction. The daily energy budgets of three species of glossophagine bats, for example, are 40–50 kJ whereas those of insects are orders of magnitude smaller (Horner et al., 1998; Winter and von Helverson, 2001). Bat pollination occurs at night, and the characteristics of bat-pollinated flowers usually differ substantially from those of diurnally pollinated flowers in terms of timing of floral anthesis, flower colour and size, and nectar odour and volume. The structure of bat-pollinated flowers, including methods of flower presentation, often differs substantially from those of their non-bat-pollinated ancestors or sister-species (Faegri and van der Pijl, 1979; Dobat and Peikert-Holle, 1985; Endress, 1994). Differences in the floral morphology and biology of species of Musa that are pollinated either by bats or by birds are especially striking. Musa acuminata, which is pollinated by the specialized pteropodid Macroglossus sobrinus, has pendant infloresences with dark purple bracts and nocturnal flowers that produce a jelly-like nectar containing 22–25 % sugar. In contrast, the diurnal flowers of M. salaccensis, which are pollinated by sunbirds, occur on erect infloresences with pink–purple bracts and produce relatively dilute nectar of 18–21 % sugar (Itino et al., 1991).
What are the evolutionary advantages of bat pollination that have led to the independent evolution of this pollination mode in numerous plant lineages? In what ways does bat pollination differ fundamentally from that of insect or bird pollination? We propose that bats differ from insects and birds in at least two ways that affect their effectiveness as pollinators: (1) they often carry large amounts of pollen on their bodies and deposit a large number of pollen grains on stigmas per flower visit and (2) they routinely carry pollen substantial distances among flowers. Muchhala (2006b) compared pollen deposition on flowers of nine species of Burmeistera by glossophagine bats and hummingbirds and found that bats deposited about 22 times more pollen on stigmas, on average, than hummingbirds. Likewise, Molina-Freaner et al. (2003) reported that the glossophagine bat Leptonycteris curasoae deposited a few thousand to over 20000 pollen grains per night on stigmas of the columnar cactus Pachycereus pringlei. Deposition of large numbers of pollen grains per stigma can be advantageous to plants for at least two reasons: (1) it ensures that enough pollen is available per flower to fertilize all ovules and (2) it fosters strong pollen–pollen competition for access to ovules.
In addition to depositing large amounts of pollen on plant stigmas, bats also deposit conspecific pollen grains of several different genotypes (i.e. different potential fathers) on stigmas. In bat-pollinated Pachira quinata, for instance, the number of pollen fathers in fruits from trees in continuous forest in Costa Rica was 2–3 compared with 1–2 pollen fathers per fruit in trees in forest fragments; levels of biparental inbreeding (i.e. mating between close relatives) were higher in the forest fragment trees than in the continuous forest (Fuchs et al., 2003). Multiple sires per fruit have also been reported in other neotropical bat-pollinated trees, including Caryocar brasiliense, Ceiba pentandra and Hymenaea courbaril (Collevatti et al., 2001; Dunphy et al., 2004; Lobo et al., 2005). Bats also commonly carry more than one species of pollen on their bodies while foraging (e.g. Heithaus et al., 1975; von Helversen and Winter, 2003; Muchhala, 2006b; Muchhala et al., 2009) but whether this interferes significantly with pollination is not currently known. Sympatric species of Burmeistera avoid potential problems associated with heterospecific pollen by placing pollen on different parts of the heads of Anoura bats (Muchhala and Potts, 2007; Muchhala, 2008).
In addition to carrying large amounts of pollen of multiple genotypes, bats often move pollen substantial distances between plants, which increases the size of genetic neighbourhoods and reduces levels of genetic subdivision between plant populations. Data summarized in Ward et al. (2005), for example, indicate that phyllostomid bats carry pollen substantially longer distances (up to 18 km) within populations of tropical trees than hummingbirds (but not necessarily longer distances than some insects). Bats are particularly effective pollinators for plants that occur at low densities [e.g. in canopy trees in the Bombacaceae s.s., arid-zone columnar cacti (except in the Tehuacan Valley of Mexico where adult cactus densities can exceed 1000 per ha; Valiente-Baunet et al., 1996) and agaves, and epiphytes in general (e.g. Tschapka, 2004)]. Ashton (1998) noted that in Bornean forests, consistently rare species of canopy trees with large fruit such as certain legumes, Neesia, Coelostegia and Durio are pollinated by large, low-fecundity and long-lived animals such as pteropodid bats and Xylocopa bees. In the genus Durio, species in subgenus Boscia are abundant small subcanopy or canopy trees that are pollinated by meliponine bees whereas species in the subgenus Durio are low-density canopy trees whose flowers are bat-pollinated. Theoretically, chronically low-density, animal-pollinated plants are expected to provide larger energy rewards per flower to attract pollinators than high-density plants (Heinrich and Raven, 1972). This could pre-adapt some low-density plants for pollination by bats and other long-distance pollinators.
If bats are such good pollinators, why are bat-pollinated flowers not more common among angiosperms? The answer to this question probably involves the costs and benefits of bat pollination to plants relative to those associated with other modes of pollination in addition to phylogenetic constraints such as flower size. Costs involved in bat pollination in terms of resources invested in flowers, inflorescences, nectar and pollen are likely to be substantial. In his survey of nectar production in a Costa Rican dry tropical forest, for example, Opler (1983) showed that floral biomass and nectar volume of bat-pollinated flowers differed from those of flowers pollinated by hummingbirds, bees and butterflies (but not hawkmoths) by several orders of magnitude. Similarly, Fleming (2002) reported that among cactus flowers, bat-pollinated species generally produced 8–20 times more calories of nectar per flower than those pollinated by hawkmoths and hummingbirds. These data suggest that bat flowers are energetically expensive, which probably represents a significant constraint to their evolution when energy for flower production is limited.
A second constraint to the evolution of bat flowers is the general phylogenetic conservatism of flower evolution in angiosperms. Insect pollination is ancestral in many families of angiosperms, and pollination by birds or bats is derived. Unless environmental conditions such as low temperatures in mountains reduce the abundance or reliability of insects (Cruden 1972), selection favouring a shift from insect to vertebrate pollination is not likely to occur. Examples of these kinds of shifts include the preponderance of hummingbird pollination in Bromeliaceae and many other families in montane regions in South and Central America and the numerous shifts from insect to hummingbird pollination in many lineages of plants in the montane west of North America (Grant, 1994; Kessler and Krömer, 2000; Luteyn, 2002). Furthermore, given that bat-pollinated flowers tend to be larger and energetically more expensive than bird flowers, which reflects the generally larger size of nectar-feeding bats compared with nectar-feeding birds worldwide (Fleming and Muchhala, 2008), selection is more likely to favour the evolution of bird flowers than bat flowers in most situations favouring a shift from insect to vertebrate pollination. In support of this, many more angiosperm families contain bird-pollinated genera and species than bat-pollinated taxa (Fleming and Muchhala, 2008). In the end, although floral and pollinator conservatism probably prevails in angiosperms, the evolution of pollination systems can also be opportunistic so that many plant families have evolved derived modes of pollination involving vertebrates. Although birds appear to be the vertebrates of choice as pollinators for many plant families, probably because of their abundance, diversity and generally small size, bats clearly offer some advantages as pollinators. As a result, bat pollination has evolved numerous times across angiosperm phylogeny.
Besides its evolutionary implications, long-distance pollination by bats also has important conservation implications. Human disturbance in the tropics and elsewhere often fragments plant populations and increases the distance between conspecifics. Without long-distance pollinators, plants with self-compatible or mixed mating systems are likely to experience higher rates of self-fertilization within habitat fragments than plants in continuous forests. Isolated self-incompatible plants (the most common mating system in tropical plants; Bawa, 1992) will fare even worse because they require pollen from another plant to set any fruit and seeds at all. Studies of canopy trees in continuous and fragmented forests in Brazil, Costa Rica, Mexico and Puerto Rico provide support for these generalizations (Gribel et al., 1999; Collevatti et al., 2001; Fuchs et al., 2003; Quesada et al., 2003; Dunphy et al., 2004). Thus, bat pollination, along with pollination by other kinds of long-distance pollinators, can serve to ‘rescue’ plants from some of the adverse effects of habitat fragmentation.
About 85 % of the cases of bat pollination appear to have evolved independently at the level of angiosperm family. A particularly striking example of this pattern is the occurrence of bat-pollinated flowers in only one hemisphere or the other in many pantropically distributed plant families. An exception to this pattern occurs in the monocot order Zingiberales in which bat pollination is widespread among related families. The common occurrence of bat pollination in the monocots, and especially the Zingiberales, may be due to the concentration of many of these taxa in the tropics, particularly the large succulent and/or arborescent species in which bat pollination almost exclusively occurs. Of the seven families of monocots in which more than a single species is bat-pollinated (Table 1), all are exclusively tropical in distribution. In addition, many of these same taxa have large flowers (Strelitziaceae) and/or large floral displays (Agavaceae, Arecaceae, Pandanaceae) in closely related taxa that are bird- or insect-pollinated. In the Zingiberales, bat pollination is concentrated in the tropical genera with large, accessible flowers that produce copious amounts of nectar and pollen (i.e. Musa, Ensete, Phenakospermum, Heliconia), all adaptations for visitation by large pollinators. Bat pollination is rare or absent in the ‘ginger families’ with more restrictive floral morphology, reduced stamen numbers and smaller nectaries (i.e. Zingiberaceae, Costaceae, Marantaceae, and Cannaceae; Kress and Specht, 2005). This same pattern – the evolution of bat pollination in large-flowered plant lineages – may also be found in the tropical Bombacaceae s.s., Bromeliaceae, Gesneriaceae, Malvaceae and possibly Bignoniaceae (Table 5).
Bat pollination occurs in about twice as many genera and species in the New World than in the Old World, despite the fact that pteropodid bats, including specialized nectar-feeders, are likely to be significantly older evolutionarily than specialized nectar-feeding phyllostomids. One reason for this is that the neotropical angiosperm flora is much richer in species, genera and families than are the floras of Africa, Asia and Australasia (Whitmore, 1998; Morley, 2000). But this explanation only begs the question, why is the neotropical flora richer than those in other tropical areas? Gentry's (1982) widely cited explanation for this emphasized the importance of Andean orogeny as a generator of exceptional plant species diversity, particularly among understorey shrubs, epiphytes and palmettos of Gondwanan ancestry. Andean-associated families such as Bromeliaceae, Campanulaceae, Cactaceae, Gesneriaceae, Marcgraviaceae and Solanaceae are relatively rich in bat-pollinated genera and/or species. Only bat-pollinated canopy trees in the Bombaceae s.s. and Fabaceae are not strongly associated with the Andes. Interestingly, whereas hummingbirds have radiated extensively in the Andes (Bleiweiss, 1998a, b; McGuire et al., 2007), the same is not true for glossophagine bats in which species of only 1–2 genera (e.g. Anoura and Platalina) occur at mid- to high elevations (Koopman, 1981). All hummingbirds have the capacity to undergo torpor while glossophagine bats do not (McNab, 2002; but see Kelm and von Helversen, 2007). The ability to undergo torpor and to reduce energy demands significantly while still maintaining high body temperatures when active has enabled hummingbirds to radiate extensively under conditions of low ambient temperatures and flowers that offer low energetic rewards in the Andes (Altshuler et al., 2004). The inability to undergo torpor has probably constrained the radiation of glossophagine bats in montane environments.
Another reason for the higher diversity of bat-pollinated plants in the Neotropics than in the Paleotropics probably reflects the small size and hovering ability of glossophagines. Large, non-hovering pteropodids and their New World counterparts, non-glossophagine phyllostomid bats, often visit large, sturdily built flowers many of which are exserted well away from foliage on erect stalks or long pendants (Figs 2–4). In contrast, small hovering glossophagines often visit small, delicate flowers that may or may not be exserted well away from foliage. The ability to hover has allowed these bats to interact with small flowers produced by a wider range of growth habits, including epiphytes and shrubs that produce small flowers as well as large-flowered canopy trees, than pteropodids (Fleming and Muchhala, 2008). We assume that it is cheaper for plants to produce small flowers than large flowers. If this is true, then it should be easier for selection to modify insect-pollinated flowers to attract small hovering glossophagines than to attract larger non-hovering phyllostomids or pteropodids. The presence of small hovering bats (and birds) in the New World has thus expanded the range of possible pollinator niches for neotropical plants. The absence of such vertebrate pollinators in the Old World has probably constrained the range of vertebrate pollination niches in angiosperms there.
Finally, we note that while the overall species richness of bat-pollinated plants is relatively modest, the ecological and economic importance of these plants is considerable. From an ecological perspective, bat-pollinated plants are conspicuous members of various New World habitats, including deserts and other arid to semi-arid habitats (e.g. columnar cacti and paniculate agaves) and dry and wet tropical forests (e.g. canopy trees of the Bombacaceae s.s.). Similarly, members of the Bombacaceae s.s. are conspicuous members of certain African and Madagascan habitats, and species of Sonneratia are important members of south-east Asian mangrove communities. From an economic perspective, many of these same taxa or their cultivated relatives have considerable monetary value. For example, fruits of bat-pollinated columnar cacti are widely harvested in many parts of the Americas (Yetman 2007), and tequila, which is derived from Agave tequilana, is a major cultural icon and agricultural industry in Mexico. Ceiba pentandra is an important source of fibre worldwide, and species of neotropical Ochroma are renowned for their lightweight wood. In south-east Asia, economically important fruits come from bat-pollinated Durio zibethinus and two species of Parkia, and bat-pollinated species of Eucalyptus are important timber trees in Australia (Fujita and Tuttle, 1991). Although domestic bananas (Musa species) produce fruit parthenocarpically, their wild relatives are bat-pollinated (and dispersed).
In conclusion, bat pollination has evolved independently in many advanced orders and families of angiosperms. It is particularly common in lowland habitats throughout the tropics but is also common in arid tropical and subtropical habitats in the New World, particularly in the Agavaceae and Cactaceae. As noted above, a number of ecologically or commercially important tropical trees, especially those in the Bombacaceae s.s., as well as many large herbaceous or arborescent plants in the monocot order Zingiberales are bat-pollinated. In the New World tropics, many epiphytes in the Bromeliaceae, Cactaceae and Gesneriaceae rely on bats for pollination. The evolution of bat-pollinated lineages probably began in the Miocene, well after the first appearance of families that currently contain many such lineages. Bat pollination is thus derived in most plant groups, and its evolution has entailed significant changes in the timing of anthesis, morphology, biochemistry and physiology of flowers. We propose that bat pollination has been particularly likely to evolve in plants that occur in chronically low densities and that from a conservation viewpoint it is a particularly valuable adaptation in landscapes in which plant populations have recently become fragmented owing to habitat destruction. The loss of nectar-feeding bats in tropical and subtropical habitats would probably have profound ecological and evolutionary effects on their food plants and on the plant communities in which they occur.
CODA: WHERE DO WE GO FROM HERE?
Our knowledge about the occurrence of bat pollination in tropical and subtropical plants has increased substantially in the past few decades but there is still much more to be learned on both sides of this fascinating mutualism. On the bat side, we need more studies on the foraging behaviour (foraging routes and food choices) of flower-visiting bats. Do these bats forage in an energetically efficient manner, as predicted by optimal foraging theory? Do they routinely rely on spatial memory to locate flowering plants? To what extent do foraging decisions made by bats conflict with the reproductive interests of plants? As one example, the foraging behaviour of the arid-zone phyllostomid Leptonycteris curasoae appears to be energetically suboptimal because it involves long commute flights from day roosts (up to 30+ km) and large, overlapping foraging areas (up to 2·5+ km2) containing much more energy and pollen from cactus flowers than is needed to support one or more individuals (Horner et al., 1998). Why is this? From the perspective of cactus flowers pollinated by this bat, this behaviour is beneficial because it provides great mobility for pollen and genes within and between populations (Hamrick et al., 2002). These strong-flying bats are therefore excellent out-crossers (Molina-Freaner et al., 2003). But we do not yet know whether all or most nectar-feeding bats are excellent out-crossers because the genetic consequences of bat pollination have rarely been documented, especially in the Old World tropics. Available data on the foraging behaviour of specialized pteropodid bats (e.g. Syconycteris australis, Macroglossus minimus, Eonycteris spelaea and Melonycteris melanops ) suggest that, except for E. spelaea, these bats are short-distance commuters that feed in small home ranges of less than 10 ha (Winkelman et al., 2000, 2003; Bonaccorso et al., 2005). They are not likely to provide nearly as much long-distance mobility for pollen and genes as does L. curasoae or their opportunistic pteropodid relatives, but genetic studies to document this are lacking.
On the plant side, we need more information about ecological conditions that favour evolutionary switches from insect- or bird-pollination to bat-pollination. Analysis of the geographical distributions of different pollination syndromes in Bromeliaceae (Kessler and Krömer, 2000) begins to provide this kind of information, but similar studies of other plant groups are needed. In addition, more detailed information is needed about why bats are favoured as pollinators in some habitats and not others. What is it about the population and behavioural ecology of nectar-feeding bats that makes them ‘attractive’ pollinators for particular plants in particular habitats? Pollinator ‘reliability’ is often mentioned as a necessary condition for the evolution of specialized pollination systems (e.g. Valiente-Banuet et al., 1996; Waser et al., 1996), but how do we operationally define the ‘reliability'of nectar bats? Finally, we need more studies of pairs of plant species where one is bat-pollinated and the other is not to understand patterns, and ultimately the mechanisms, of character change. What is involved in the switch from diurnal to nocturnal flower anthesis? In the evolution of large corollas and nectaries? In the production of strong floral scents featuring sulphur compounds (in the New World)? Etc. It should be clear from this review that we know a lot about the natural history and phylogenetic and biogeographical distributions of nectar-feeding bats and their food plants. We now need to dig deeper into this mutualism to understand how and why it has evolved.
ACKNOWLEDGMENTS
We thank Don Levin for suggesting to us that we should write this review, portions of which were taken from a forthcoming book (The Ornaments of Life, University of Chicago Press) written by T.H.F. and W.J.K. We thank our editors at the University of Chicago Press (Christie Henry and John Thompson) for permission to use material from our book in this review. Nate Muchhala and two anonymous reviewers provided many useful suggestions for improving this paper. Bat Conservation International kindly provided the photographs for Figs 1 and 2, and Ida Lopez applied her excellent skills to composing them. T.H.F. thanks the US National Science Foundation, National Geographic Society and the Ted Turner Foundation for supporting his research on bat pollination. C.K.G. is grateful to the Beneficia Foundation and Bat Conservation International for financial support and to Scott Mori for sharing his knowledge of and enthusiasm for Neotropical plants. W.J.K. thanks the US National Science Foundation, National Geographic Society and the Smithsonian Institution for funding support.
We dedicate this review to the memory of Otto von Helversen for his substantial contributions to our knowledge of bat pollination.
APPENDIX 1
Number of nectar-feeding bats in two families. Indicated first are morphologically specialized genera (number of species in parentheses) in bold type followed by genera of opportunistic flower visitors from which pollen has been collected. Taxonomy follows Simmons (2005).
Family Pteropodidae: Eonycteris (3), Macroglossus (2), Megaloglossus (1), Melonycteris (3), Notopteris (2) and Syconycteris (3); Balionycteris, Cynopterus, Eidolon, Epomophorus, Epomops, Lissonycteris, Micropteropus, Myonycteris, Nanonycteris, Pteropus and Rousettus,
Family Phyllostomidae: Anoura (5), Brachyphylla (2), Choeroniscus (3), Choeronycteris (1), Erophylla (2), Glossophaga (5), Hylonycteris (1), Leptonycteris (3), Lichonycteris (1), Lionycteris (1), Lonchophylla (7), Monophyllus (2), Musonycteris (1), Phyllonycteris (3), Platalina (1) and Scleronycteris (1); Ametrida, Artibeus, Carollia, Chiroderma, Glyphonycteris, Micronycteris, Phyllostomus, Platyrrhinus, Rhinophylla, Sturnira, Trinycteris, Uroderma and Vampyressa.
APPENDIX 2
New World bat-pollinated species listed by plant family
(1) This list excludes species reported to be visited by bats in the New World that are introduced from the Old World (Bombax, Durio, Kigelia, Mahduca, Musa, Thespesia, Thunbergia, Zingiber); visited by bats for fruit, not nectar/pollen (Anacardium, Brosimum, Carica, Chrysophyllum, Eugenia, Manilkara, Muntingia, Solanum, Symphonia, Syzygium); known to be pollinated by wind (Acalypha, Alnus, Celtis, Pinus, Quercus) or small insects (Aristolochia, Berberis, Bursera, Theobroma); or where bat-pollination seems very doubtful (Clusia, Vanilla).
(2) Inclusion in this table does not indicate that bats pollinate all listed species throughout their ranges.
(3) Plant families follow the Angiosperm Phylogeny Group system. Species names correspond to those accepted in the Missouri Botanical Garden's VAST (VAScular Tropicos – http://mobot.mobot.org/W3T/Search/vast.html) nomenclatural database or found in the International Plant Name Index (IPNI; http://www.ipni.org). The references to all other name changes are provided in the footnotes. Genus sp. is only included when no other species represents the genus.
(4) Information gathered from the Database of Neotropical Bat/Plant Interactions (Geiselman et al., 2004 onwards).
| ACANTHACEAE |
| Harpochilus neesianus |
| Louteridium chartaceum |
| Louteridium donnell-smithii |
| Ruellia eurycodon |
| Ruellia exostemma |
| Ruellia malaca |
| Trichanthera gigantea |
| AGAVACEAE |
| Agave angustifolia |
| Agave cocui |
| Agave colimana |
| Agave deserti |
| Agave desmettiana |
| Agave grisea |
| Agave havardiana |
| Agave macroacantha |
| Agave neomexicana |
| Agave palmeri |
| Agave parryi |
| Agave salmiana1 |
| Agave schottii |
| Agave shawii |
| Agave tequilana |
| Hesperaloe sp. |
| Manfreda brachystachys |
| AMARYLLIDACEAE |
| Eustephia sp. |
| Hippeastrum calyptratum2 |
| ARECACEAE |
| Calyptrogyne ghiesbreghtiana |
| Coccothrinax sp. |
| Roystonea regia |
| ASTERACEAE |
| Cirsium subcoriaceum |
| Gongylolepis jauaensis |
| Wunderlichia cruelsiana |
| BIGNONIACEAE |
| Adenocalymna dichilum |
| Amphitecna isthmica3 |
| Amphitecna kennedyae4 |
| Amphitecna latifolia5 |
| Amphitecna spathicalyx6 |
| Crescentia alata7 |
| Crescentia amazonica |
| Crescentia cujete |
| Cydista diversifolia |
| Parmentiera cereifera |
| Parmentiera edulis |
| Parmentiera macrophylla |
| Tabebuia obtusifolia |
| Tabebuia platyantha |
| BORAGINACEAE |
| Cordia alliodora |
| Cordia gerascanthus |
| BROMELIACEAE8 |
| Encholirium glaziovii |
| Guzmania calothyrsa |
| Guzmania danielii |
| Guzmania killipiana |
| Guzmania morreniana |
| Guzmania retusa |
| Guzmania sphaeroidea |
| Pitcairnia brongniartiana |
| Pitcairnia trianae |
| Puya ferruginea |
| Vriesea bituminosa |
| Vriesea gigantea |
| Vriesea longicaulis |
| Vriesea longiscapa |
| Vriesea morrenii |
| Vriesea platynema8 |
| Vriesea sazimae2 |
| Werauhia gladioliflora9 |
| Werauhia kupperiana10 |
| Werauhia ororiensis11 |
| Werauhia rugosa12 |
| CACTACEAE |
| Browningia riosaniensis13 |
| Carnegiea gigantea |
| Cephalocereus columna-trajani14 |
| Cereus hexagonus |
| Dendrocereus nudiflorus15 |
| Echinocactus sp. |
| Harrisia sp. |
| Hylocereus undatus |
| Lemaireocereus sp. |
| Leptocereus arboreus |
| Leptocereus santamarinae |
| Leptocereus wrightii |
| Machaerocereus sp. |
| Marginatocereus marginatus |
| Monvillea smithiana16 |
| Myrtillocactus sp. |
| Neobuxbaumia euphorbioides17 |
| Neobuxbaumia macrocephala |
| Neobuxbaumia tetetzo |
| Opuntia sp. |
| Pachycereus pecten-aboriginum |
| Pachycereus pringlei |
| Pachycereus weberi |
| Pilosocereus catingicola |
| Pilosocereus chrysacanthus18 |
| Pilosocereus lanuginosus19 |
| Pilosocereus leucocephalus20 |
| Pilosocereus moritzianus21 |
| Pilosocereus tillianus2 |
| Platyopuntia sp. |
| Pterocereus gaumeri22 |
| Samaipaticereus corroanus |
| Selenicereus sp. |
| Stenocereus griseus23 |
| Stenocereus queretaroensis |
| Stenocereus stellatus |
| Stenocereus thurberi24 |
| Subpilocereus horrispinus Subpilocereus ottonis |
| Subpilocereus repandus25 |
| Weberbauerocereus weberbaueri |
| Weberocereus trichophorus |
| Weberocereus tunilla |
| CAMPANULACEAE |
| Burmeistera borjensis |
| Burmeistera ceratocarpa |
| Burmeistera cyclostigmata |
| Burmeistera cylindrocarpa |
| Burmeistera fusco-apicata |
| Burmeistera lutosa |
| Burmeistera multiflora |
| Burmeistera smaragdi |
| Burmeistera sodiroana |
| Burmeistera succulenta |
| Burmeistera tenuiflora |
| Burmeistera truncata |
| Centropogon mandonis |
| Centropogon nigricans |
| Centropogon smithii |
| Siphocampylus corynoides |
| Siphocampylus foetidus |
| Siphocampylus giganteus |
| Siphocampylus sulfureus |
| Siphocampylus tunicatus |
| CANNACEAE |
| Canna liliiflora26 |
| CAPPARACEAE |
| Capparis flexuosa |
| Capparis hastata |
| Capparis scabrida |
| Cleome anomala |
| Cleome arborea |
| Cleome moritziana |
| Cleome viridiflora |
| Crateva tapia27 |
| CARYOCARACEAE |
| Caryocar brasiliense |
| Caryocar coriaceum |
| Caryocar costaricense |
| Caryocar nuciferum |
| Caryocar villosum |
| CHRYSOBALANACEAE |
| Couepia dolichopoda |
| Couepia longipendula |
| Hirtella sp. |
| COMBRETACEAE |
| Combretum sp. |
| CONVOLVULACEAE |
| Ipomoea ampullacea |
| Ipomoea neei28 |
| Ipomoea wolcottiana29 |
| CUCURBITACEAE |
| Calycophysum pedunculatum |
| Calycophysum spectabile30 |
| Cayaponia sp. |
| Cucurbita argyrosperma |
| Lagenaria siceraria |
| ERICACEAE |
| Arbutus sp. |
| EUPHORBIACEAE |
| Croton sp. |
| Hura crepitans |
| Mabea occidentalis |
| FABACEAE |
| Acacia farnesiana |
| Albizzia occidentalis |
| Alexa grandiflora |
| Bauhinia angulicaulis |
| Bauhinia glabra |
| Bauhinia multinervia31 |
| Bauhinia pauletia |
| Bauhinia rufa32 |
| Bauhinia siqueiraei |
| Bauhinia ungulata33 |
| Browneopsis cauliflora |
| Browneopsis disepala |
| Browneopsis macrofoliolata |
| Browneopsis ucayalina |
| Caesalpinia bahamensis |
| Caesalpinia vesicaria |
| Calliandra calothyrsus34 |
| Calliandra formosa |
| Calliandra grandiflora35 |
| Calliandra tweediei36 |
| Conzattia sp. |
| Dichrostachys cinerea |
| Elizabetha leiogyne |
| Elizabetha paraensis |
| Elizabetha speciosa |
| Eperua falcata |
| Eperua leucantha |
| Eperua stipulata37 |
| Erythrina fusca38 |
| Hymenaea courbaril |
| Hymenaea stigonocarpa |
| Inga bahiensis |
| Inga cayennensis |
| Inga marginata |
| Inga sessilis |
| Inga spectabilis |
| Inga vera |
| Jacqueshuberia purpurea |
| Jacqueshuberia quinquangulata |
| Lonchocarpus sp. |
| Lysiloma latisiliquum |
| Mimosa lewisii |
| Mucuna holtonii39 |
| Mucuna mutisiana |
| Mucuna pruriens |
| Mucuna rostrata |
| Mucuna sloanei |
| Mucuna urens40 |
| Ormosia sp. |
| Parkia cachimboensis |
| Parkia decussata |
| Parkia discolor41 |
| Parkia gigantocarpa |
| Parkia igneiflora |
| Parkia nitida42 |
| Parkia panurensis43 |
| Parkia pendula |
| Parkia platycephala |
| Peltophorum adnatum |
| GENTIANACEAE |
| Chelonanthus alatus44 |
| Gentiana sp. |
| Macrocarpaea duquei |
| Macrocarpaea glabra |
| Macrocarpaea macrophylla45 |
| Macrocarpaea polyantha |
| Macrocarpaea quelchii46 |
| Symbolanthus latifolius |
| GERANIACEAE |
| Geranium sp. |
| GESNERIACEAE |
| Drymonia sp. |
| Gesneria alpina |
| Gesneria calycina |
| Gesneria calycosa |
| Gesneria clandestina |
| Gesneria exserta |
| Gesneria fruticosa |
| Gesneria gloxinioides |
| Gesneria onychocalyx |
| Gesneria pedunculosa |
| Gesneria pumila |
| Gesneria shaferi |
| Gesneria viridiflora |
| Kohleria tigridia47 |
| Paliavana prasinata |
| Paliavana sericiflora |
| Paliavana werdermannii |
| Rhytidophyllum grande |
| Rhytidophyllum tomentosum |
| Sinningia brasiliensis48 |
| LAMIACEAE |
| Catopheria chiapensis |
| Salvia sp. |
| LECYTHIDACEAE |
| Lecythis barnebyi |
| Lecythis brancoensis |
| Lecythis poiteaui |
| LORANTHACEAE |
| Psittacanthus acinarius |
| LYTHRACEAE |
| Lafoensia acuminata49 |
| Lafoensia densiflora |
| Lafoensia glyptocarpa |
| Lafoensia pacari |
| Lafoensia punicifolia |
| Lafoensia replicata50 |
| Lafoensia vandelliana |
| MALVACEAE |
| Abutilon bedfordianum |
| Abutilon niveum |
| Abutilon pedrae-brancae |
| Abutilon peltatum |
| Abutilon regnellii |
| Abutilon rufinerve |
| Anoda sp. |
| Anotea flavida51 |
| Bakeridesia sp.52 |
| Berrya cubensis53 |
| Bombacopsis squamigera |
| Ceiba aesculifolia54 |
| Ceiba pentandra |
| Ceiba speciosa55 |
| Ceiba trichistandra |
| Chiranthodendron pentadactylon |
| Eriotheca pentaphylla |
| Helicteres baruensis |
| Helicteres rekoi |
| Hibiscus clypeatus |
| Hibiscus elatus |
| Luehea alternifolia56 |
| Luehea candida |
| Luehea grandiflora |
| Luehea paniculata |
| Matisia bracteolosa |
| Matisia cordata |
| Ochroma pyramidale57 |
| Pachira aquatica |
| Pachira quinata58 |
| Pseudobombax ellipticum |
| Pseudobombax grandiflorum |
| Pseudobombax longiflorum |
| Pseudobombax septenatum |
| Quararibea asterolepis |
| Quararibea gomeziana |
| Quararibea ochrocalyx |
| Quararibea parvifolia |
| Quararibea pendula |
| Wercklea insignis |
| Wercklea lutea59 |
| MARCGRAVIACEAE |
| Marcgravia brownei |
| Marcgravia comosa |
| Marcgravia coriacea60 |
| Marcgravia dressleri |
| Marcgravia evenia2 |
| Marcgravia helverseniana |
| Marcgravia longifolia |
| Marcgravia mexicana |
| Marcgravia myriostigma |
| Marcgravia nepenthoides |
| Marcgravia nervosa |
| Marcgravia pittieri |
| Marcgravia polyantha |
| Marcgravia serrae |
| Marcgravia trinitatis61 |
| Marcgraviastrum macrocarpum |
| Norantea sp. |
| MELASTOMATACEAE |
| Meriania pichinchensis |
| Purpurella grossa62 |
| NYCTAGINACEAE |
| Bougainvillea spectabilis |
| Mirabilis longiflora |
| ONAGRACEAE |
| Oenothera sp. |
| PASSIFLORACEAE |
| Passiflora galbana |
| Passiflora mucronata |
| Passiflora penduliflora |
| Passiflora recurva |
| Passiflora ovalis63 |
| POLEMONIACEAE |
| Cobaea aschersoniana |
| Cobaea gracilis64 |
| Cobaea scandens |
| Cobaea trianae |
| PROTEACEAE |
| Roupala sp. |
| RUBIACEAE |
| Condaminea corymbosa |
| Hillia illustris |
| Palicourea sp. |
| SALICACEAE |
| Salix sp. |
| SAPINDACEAE |
| Cupania sp. |
| SCROPHULARIACEAE |
| Eremogeton grandiflorus |
| SOLANACEAE |
| Datura inoxia |
| Dyssochroma viridiflora |
| Juanulloa verrucosa65 |
| Merinthopodium dressleri66 |
| Merinthopodium neuranthum67 |
| Merinthopodium pendulum68 |
| Merinthopodium vogelii69 |
| Nicotiana otophora |
| Nicotiana tomentosa |
| Solandra guerrerensis |
| Solandra maxima |
| Trianaea nobilis |
| Trianaea speciosa70 |
| STRELITZIACEAE |
| Phenakospermum guyannense |
| VELLOZIACEAE |
| Barbacenia rubro-virens |
| VERBENACEAE |
| Citharexylum sp. |
| Lantana sp. |
| VOCHYSIACEAE |
| Vochysia sp. |
1Cited as Manfreda saliama by Eguiarte et al. (1987), but must refer to Agave saliama. 2Not recognized by Tropicos but is by Index Kewensis. 3Dendrosicus isthmicus = basionym. 4Dendrosicus kennedyi = basionym. 5Synonym of Dendrosicus latifolius and Enallagma latifolia. 6Dendrosicus spathicalyx = basionym. 7Synonym of Parmentiera alata. 8Cited as Vriesea moehringiana by Dobat and Peikert-Holle (1985), but must refer to V. platynema. 9Synonym of Vriesea gladioliflora. 10Vriesea kupperiana = basionym. 11Synonym of Thecophyllum irazuense and Vriesea irazuense. 12Synonym of Vriesea rugosa. 13Rauhocereus riosaniensis = basionym. 14Synonym of Cephalocereus hoppenstedtii. 15Cited as Acanthocereus nudiflorus by Simmons and Wetterer (2002), but must refer to Dendrocereus nudiflorus. 16Cephalocereus smithiana = basionym. 17Synonym of Cephalocereus euphorbioides. 18Synonym of Cephalocereus chrysacanthus. 19Synonym of Pilocereus lanuginosus. 20Synonym of Cephalocereus leucocephalus, C. palmeri and C. sartorianus. 21Synonym of Cephalocereus moritzianus. 22Synonym of Pachycereus gaumeri. 23Synonym of Cereus griseus, Lemaireocereus griseus and Ritterocereus griseus. 24Synonym of Lemaireocereus thurberi. 25Synonym of Cereus atroviridis, C. grenadensis, C. repandus and Samaipaticereus peruvianus. 26Synonym of Canna brittonii. 27Synonym of Crateva benthamii. 28Synonym of Ipomoea peduncularis. 29Synonym of Ipomoea arborescens. 30Synonym of Edmondia spectabilis (Asteraceae). 31Synonym of Bauhinia megalandra. 32Synonym of Bauhinia holophylla. 33Synonym of Bauhinia macrostachya. 34Synonym of Calliandra confusa. 35Synonym of Calliandra anomala. 36Synonym of Calliandra guildingii. 37Synonym of Eperua schomburgkiana. 38Synonym of Erythrina glauca. 39Synonym of Mucuna andreana. 40Synonym of Mucuna altissima. 41Synonym of Parkia auriculata. 42Synonym of Parkia alliodora, P. inundabilis and P. oppositifolia. 43Synonym of Parkia pectinata. 44Synonym of Irlbachia alata, Lisianthius alatus, L. cheloniodes and L. viridiflorus. Struwe et al. (2002) determined that the accepted name is Chelonanthus alatus. 45Synonym of Lisianthius macrophyllus and Macrocarpaea valerioi. 46Lisianthius quelchii = basionym. 47Synonym of Capanea grandiflora, C. oerstedii and C. picturata. 48Synonym of Lietzia brasiliensis. 49Synonym of Lafoensia speciosa. 50Could be a subspecies of Lafoensia vandelliana. 51Synonym of Malvaviscus acerifolius. 52Cited as Bakeridesia paulistana by Dobat and Peikert-Holle (1985), but this name is not recognized by Tropicos or IPNI. 53Synonym of Carpodiptera cubensis. 54Synonym of Ceiba acuminata and C. grandiflora. 55Synonym of Chorisia speciosa. 56Synonym of Luehea speciosa. 57Synonym of Ochroma lagopus. 58Synonym of Bombacopsis fendleri and B. quinata. 59Synonym of Hibiscus luteus. 60Synonym of Marcgravia cuyuniensis. 61Synonym of Marcgravia rectiflora. 62Purpurella included in Tibouchina by Renner (1989). 63Synonym of Tetrastylis ovalis (Feuillet and MacDougal, 2007). 64Synonym of Cobaea panamensis. 65Synonym of Markea verrucosa (Knapp et al., 1997). 66Merinthopodium is a synonym of Markea (Knapp et al., 1997). 67Synonym of Markea campanulata, M. internexa and M. neurantha (Knapp et al., 1997). 68Synonym of Markea pendula (Knapp et al., 1997). 69Synonym of Markea vogelii (Knapp et al., 1997). 70Synonym of Trianaea spectabilis (Knapp et al., 1997).
APPENDIX 3
Old World Bat-pollinated species listed by plant family
(1) This list excludes species visited by bats for fruit, not nectar/pollen (Calophyllum, Carica, Cerbera, Chlorophora, Mammea, Mangifera, Morus, Palaquium hispidum, Syzygium inophylloides, Terminalia); those known to be pollinated by small insects (Arenga, Celtis, Cocos, Diospyrus, Elaeagnus, Rhaphiolepis, Tamarix, Trema) or wind (Casuarina, Dendrocnidne, Pipturus, Tamarix); those introduced in areas where bats have been recorded visiting them (Agave, Callistemon citrinus, Ceiba, Crescentia, Hevea, Ochroma, Pachira, Parmentiera, Ravenala madagascariensis, Samanea saman); or those whose flowers are destroyed instead of pollinating by bats (Eria obusta, Eucalyptus spp.). (See footnote †, below table.)
(2) Inclusion in this appendix does not indicate that bats pollinate all listed species throughout their ranges.
(3) Plant families follow the Angiosperm Phylogeny Group system. Species names correspond to those accepted in the Missouri Botanical Garden's VAST (VAScular Tropicos) nomenclatural database or the International Plant Name Index. Genus sp. is only included when no other species represents the genus.
| ACANTHACEAE |
| Avicennia sp.T |
| ANACARDIACEAE |
| Rhus taitensisT, E |
| ANNONACEAE |
| Cananga odorataD, E |
| APOCYNACEAE |
| Alstonia actinophyllaT |
| Cerbera oppositifolia*I, S |
| Neisosperma sp.D |
| ARALIACEAE |
| Polyscias samoensisE |
| ARECACEAE |
| Areca sp.*I, S |
| Livistona chinensisT |
| Carpentaria acuminataT |
| Gulubia sp.T |
| ASPHODELACEAE |
| Aloe dolomiticaI, S, T |
| ASTELIACEAE |
| Collospermum samoenseT |
| BIGNONIACEAE |
| Fernandoa sp.I |
| Haplophragma adenophyllumI, AA |
| Heterophragma roxburghii1, I, T |
| Kigelia africana2, A, C, I, Z, AA |
| Markhamia stipulata3, D, Z, AA |
| Nyctocalos sp.*G, I, S |
| Oroxylum indicumG, I, K, S, T, Y, Z, AA |
| Pajanelia longifolia4, I, Y, Z |
| Spathodea campanulataA, E, I, T |
| Stereospermum xylocarpum5, I, T |
| CAMPANULACEAE |
| Lobelia sp.T |
| CELASTRACEAE |
| Cassine sp.T |
| CHRYSOBALANACEAE |
| Maranthes aubrevilleiT, U |
| Maranthes corymbosaW |
| Maranthes polyandra6, I, P, T |
| CLUSIACEAE |
| Pentadesma butyraceT, U |
| COMBRETACEAE |
| Lumnitzera littoreaT |
| CONVOLVULACEAE |
| Erycibe micrantha7, I, AA |
| Ipomoea albivenia*I, S, AA |
| ELAEOCARPACEAE |
| Elaeocarpus rarotongensisI, T |
| Elaeocarpus tonganusE |
| Elaeocarpus ulianusE |
| EUPHORBIACEAE |
| Glochidion ramiflorumE, I, T |
| Macaranga tanariusT |
| FABACEAE |
| Bauhinia hookeri8, I, S |
| Castanospermum australe*I, S, T, X |
| Cynometra sp.T |
| Daniellia oliveriI, S, U, Z |
| Erythrina fuscaT |
| Erythrina variegata9*E, I, S |
| Inocarpus sp.*T |
| Intsia bijugaT |
| Mucuna flagellipesI, T |
| Mucuna giganteaI, T, AA |
| Mucuna junghuhnianaI, AA |
| Mucuna macropodaN |
| Mucuna monospermaI, AA |
| Mucuna pruriensZ, AA |
| Mucuna reticulataI, AA |
| Parkia bicolorI, L, N, T |
| Parkia biglandulosaF |
| Parkia biglobosaC, D, F, N |
| Parkia clappertonianaA, B, C, I, T |
| Parkia filicoideaI, N |
| Parkia javanicaI, M, Y |
| Parkia singularisI, Y |
| Parkia speciosaC, K, M, N, Y, AA |
| Parkia timoriana10, I, N, T, AA |
| Erythrophleum sp.T |
| Sesbania formosaD |
| HELICONIACEAE |
| Heliconia indicaZ |
| Heliconia papuanaZ |
| Heliconia solomonensisO, T |
| LAURACEAE |
| Neolitsea sp.T |
| LECYTHIDACEAE |
| Abdulmajidia sp.V |
| Barringtonia asiatica11, E, I, T, Z |
| Careya arborea*G, S |
| Foetidia mauritiana*I |
| Planchonia careyaT |
| LOGANIACEAE |
| Fagraea sp.12, S, T |
| LORANTHACEAE |
| Amyema sp.T |
| Loranthus sp.*I, S, T, X |
| LYTHRACEAE |
| Duabanga grandiflora13, I, T, Y, Z |
| Duabanga moluccanaI, X, AA |
| Sonneratia alba14, I, T, Y, Z, AA |
| Sonneratia apetala15, I, Y, Z |
| MALVACEAE |
| Adansonia digitataA, C, I, P, T, Z, AA |
| Adansonia gibbosa16, I, AA |
| Adansonia grandidieriD, Z |
| Adansonia madagascariensisAA |
| Bombax buonopozenseT |
| Bombax ceiba17, I, T, Z, AA |
| Bombax valetoniiI, Y, AA |
| Ceiba pentandraA, B, C, E, I, J, Y, Z, AA |
| Cullenia excelsaI |
| Dombeya sp.AA |
| Durio carinatusI |
| Durio graveolensI, Y, Z |
| Durio kutejensisI, Z, AA |
| Durio malaccensisD |
| Durio zibethinusI, K, Y, Z, AA |
| Kostermansia sp.S |
| MELIACEAE |
| Azadirachta indica18*A, I, T |
| Dysoxylum gaudichaudianumT |
| MORACEAE |
| Artocarpus sp.*I, T, Y |
| MUSACEAE |
| Ensete glaucumI |
| Ensete ventricosumI |
| Musa acuminata19, I, K, BB |
| Musa balbisianaI |
| Musa coccineaAA |
| Musa itineransR |
| Musa paradisiacaI, AA |
| Musa textilisI, T, AA |
| MYRTACEAE |
| Angophora costata*I, T |
| Angophora subvelutina*I, X |
| Angophora woodsiana20*I, X |
| Callistemon pachyphyllus*I, T |
| Callistemon salgnus*I, S |
| Leptospermum sp.* I, S, T |
| Lophostemon confertusT |
| Lophostemon grandiflorusT |
| Lophostemon lactifluusT |
| Melaleuca argentea*T |
| Melaleuca cajuputi*T |
| Melaleuca dealbata*T |
| Melaleuca leucadendra21*I, T |
| Melaleuca nervosa*T |
| Melaleuca quinquenervia*I, T |
| Metrosideros vera*I |
| Metrosideros villosa*T |
| Syncarpia glomulifera22*I, T, X |
| Syncarpia hillii*I, T |
| Syzygium cormiflorum*I |
| Syzygium cumini23, T, AA |
| Syzygium dealatum*E |
| Syzygium jambos*I, T |
| Syzygium malaccense24, E, T, AA |
| Syzygium richii*E, T |
| Syzygium samarangense25, I, T, AA |
| Syzygium tierneyanum*I |
| PANDANACEAE |
| Freycinetia insignisI, AA |
| Freycinetia reineckeiE |
| Pandanus fragransT |
| Pandanus tectoriusE, T |
| PROTEACEAE |
| Banksia integrifoliaI, Q, T, X |
| Banksia roburT |
| Banksia serrata26, T, X |
| Grevillea pteridifoliaT |
| Grevillea robustaI, T |
| Protea elliottiiI, P, T |
| RHAMNACEAE |
| Alphitonia sp.E |
| RHIZOPHORACEAE |
| Rhizophora sp.*I, S, T |
| ROSACEAE |
| Eriobotrya sp.T |
| RUBIACEAE |
| Aidia sp.T |
| Guettarda speciosaE, T |
| Neonauclea forsteriE, T |
| SALICACEAE |
| Populus sp.T |
| SALVADORACEAE |
| Salvadora persicaT |
| SAPINDACEAE |
| Diploglottis cunninghamiiT |
| Tristiropsis sp.T |
| SAPOTACEAE |
| Madhuca beccarii27, G |
| Madhuca indica28, F, G, I, T, AA |
| Madhuca macrophyllaAA |
| Manilkara hexandra29, I, S, T |
| Palaquium gutta30, I, AA |
| Palaquium obovatumM |
| Palaquium quercifolium*I, S, AA |
| Palaquium stehliniiE |
| Payena macrophyllaI |
| Planchonella samoensisE |
| Planchonella torricellensis*I, S, T |
| Tieghemella heckelii31, H, AA |
| Vitellaria sp.T |
| SOLANACEAE |
| Physalis sp.T |
| XANTHORRHOEACEAE |
| Xanthorrhoea sp.T |
*Indicates where authors have doubted if bat visitation affects pollination.
1Synonym of Heterophragma quadriloculare. 2Synonym of Kigelia aethiopica and K. pinnata. 3Synonym of Dolichandrone cauda-felina and D. stipulata. 4Synonym of Pajanelia multijuga. 5Stereospermum is a synonym of Radermachera. 6Synonym of Parinari polyandra. 7Synonym of Erycibe ramiflora. 8Synonym of Lysiphyllum hookeri. 9Synonym of Erythrina lithosperma. 10Synonym of Parkia roxburghii. 11Synonym of Barringtonia racemosa. 12Cited as Fagraea bateriana but no species name in Tropicos and IPNI. 13Synonym of Duabanga sonneratioides. 14Synonym of Sonneratia acida and S. caseolaris. 15Synonym of Sonneratia ovata. 16Synonym of Adansonia gregorii. 17Synonym of Bombax malabaricum; Bombax is a synonym of Gossampinus. 18Synonym of Melia azadirachta. 19Includes subspecies Musa banksii and M. truncata; synonym of Musa halabanensis and M. malaccensis. 20Basionym of Angophora floribunda and A. lanceolata. 21Synonym of Melaluca viridiflora. 22Synonym of Syncarpia laurifolia. 23Synonym of Eugenia cumini. 24Synonym of Eugenia malaccensis. 25Synonym of Eugenia javanica. 26Synonym of Banksia aemula. 27Synonym of Ganua beccarii. 28Synonym of Bassia latifolia and Illipe. 29Synonym of Mimusops hexandra. 30Synonym of Dichopsis gutta. 31Synonym of Dumoria heckelii.
References: AAyensu (1974);
BBaker (1973); CBaker & Harris (1957); DBaker et al. (1998); EBanack (1998 and references therein); FBhat (1994); GCorlett (2004); HCunningham (1995b); IDobat & Peikert-Holle (1985 and references therein); JElmqvist et al. (1992); KGould (1978); LGrünmeier (1990); MHodgkison et al. (2004b); NHopkins (1983, 1984, 1993) BBItino et al. (1991); OKress (1985); PLack (1978); QLaw (1992); RLiu et al. (2002); SMarshall (1983, 1985); TMickelburgh et al. (1992 and references therein); UPettersson et al. (2004); VPrance & Mori (2004); WPrance & White (1988); XRatcliffe (1932); YStart & Marshall (1976); ZStroo (2000); AAvan der Pijl (1941; 1956, 1961)
†References used to determine legitimate pollinators of excluded species: Andersson (1998); Calley et al. (1993); Friis (1993); Gaskin (2003); Henderson (2002); Johnson & Wilson (1993); Nyhagen et al. (2005); Pennington (2004); Stevens (2007); Todzia (1993).
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