bs_bs_banner Biological Journal of the Linnean Society, 2013, 110, 199–213. With 6 figures Interactions between hawkmoths and flowering plants in East Africa: polyphagy and evolutionary specialization in an ecological context DINO J. MARTINS* and STEVEN D. JOHNSON School of Life Sciences, University of KwaZulu-Natal, Private Bag X01, Scottsville, Pietermaritzburg 3209, South Africa Received 5 December 2012; revised 6 March 2013; accepted for publication 6 March 2013 Hawkmoths (Lepidoptera, Sphingidae) are considered important pollinators in tropical regions, but the frequency and degree of reciprocal specialization of interactions between hawkmoths and flowers remain poorly understood. Detailed observations at two sites in Kenya over a two-year period indicate that adult hawkmoths are routinely polyphagous and opportunistic, regardless of their proboscis length. About 700 individuals of 13 hawkmoth species were observed visiting a wide range of plant species at the study sites, including 25 taxa that appear to be specifically adapted for pollination by hawkmoths. We estimate that 277 plant species in Kenya (c. 4.61% of the total angiosperm flora) are adapted for pollination by hawkmoths. Floral tube lengths of these plants have a bimodal distribution, reflecting the existence of two hawkmoth guilds differing in tongue length. Hawkmoths exhibited strongly crepuscular foraging patterns with activity confined to a 20-min period at dusk and, in some cases, a similar period just before dawn. Corolla tube length appears to act as a mechanical filter as the longest-tubed plants were visited by the fewest hawkmoth species and these were exclusively from the longtongued guild. Tube length showed a strong positive relationship with nectar volume, even after phylogenetic correction, which implies that plants with long corolla tubes are under selection to offer relatively large amounts of nectar to entice visits by polyphagous long-tongued hawkmoths. Our study shows that diffusely co-evolved pollination systems involving long-tongued hawkmoths are clearly asymmetrical, with plants exhibiting a high degree of floral specialization, while hawkmoths exhibit polyphagous behaviour. © 2013 The Linnean Society of London, Biological Journal of the Linnean Society, 2013, 110, 199–213. ADDITIONAL KEYWORDS: Agrius – coevolution – generalization – insect–plant interactions – Kenya – Nephele – pollination. INTRODUCTION Interactions between hawkmoths and the flowers they visit provide the most famous putative examples of the process of coevolution (Darwin, 1877; Nilsson, 1998). From this, it might be expected that these interactions are, as a rule, highly specialized. Here it is shown that hawkmoths are actually highly polyphagous foragers and, with some notable exceptions, are involved in asymmetrical relationships, with the *Corresponding author. Current Address: Turkana Basin Institute, PO Box 24467-00502, Nairobi, Kenya. E-mail: [email protected] greatest dependency and specialization occurring on the part of the plants that depend on these animals for pollination. Virtually all adult hawkmoths (Lepidoptera: Sphingidae) with functional proboscides utilize flowers as a source of food in the form of nectar. In the drylands of East Africa, flowering patterns are closely tied to rainfall (Cribb, 1984; Blundell, 1987; Agnew & Agnew, 1994; Beentje, 1994; Stewart, 1996). As rainfall is highly variable and unpredictable in the strictly seasonal parts of the region (National Atlas of Kenya, 1969), it follows that nectar resources would be similarly variable and unpredictable, thus favouring polyphagy by nectarivores. © 2013 The Linnean Society of London, Biological Journal of the Linnean Society, 2013, 110, 199–213 199 200 D. J. MARTINS and S. D. JOHNSON Synchronous flowering in strongly seasonal environments can also give rise to competition among plants for attraction of nectarivores (Cruz-Neto et al., 2011). Hawkmoths, which can gain access to nectar in most flowers because of their long tongues, are able to make foraging decisions based on rewards in flowers (Miller, 1981, 1985, 1997; Goyret, Markwell & Raguso, 2007; Riffell et al., 2008). Thus, plants specialized for hawkmoth pollination may need to offer substantial nectar rewards if they are to compete for attraction of these insects. Selection for substantial nectar rewards should be particularly strong in rare plant taxa that are specialized for hawkmoth pollination. There is evidence that insects feeding from flowers learn patterns of distribution and follow these for varying periods of time depending on the species involved (Heinrich, 1976; Papaj & Prokopy, 1989; White et al., 1994; Goyret & Raguso, 2006). Learning behaviour in hawkmoths has been demonstrated experimentally for the diurnal species Macroglossum stellatarum (Kelber, 1996, 1997; Kelber & Pfaff, 1997; Kelber, Balkenius & Warrant, 2002) as well as the nocturnal species Manduca sexta (Daly, Durtschi & Smith, 2001; Goyret et al., 2008; Riffell et al., 2008). Hawkmoths are powerful flyers and have the ability to disperse widely and visit widely spaced plants; combined with their learning behaviour, this means that hawkmoth pollinators can serve as effective pollinators, enhancing gene flow between fragmented populations of specialized plants (Kitching & Cadiou, 2000; Martins & Johnson, 2007, 2009). Interactions between hawkmoths and flowers are, in general, very poorly documented. Only four previous studies have attempted to systematically document these interactions at the level of communities or local floras and these were carried out in Costa Rica (Haber & Frankie, 1989; Agosta & Janzen, 2005), Brazil (Oliveira, Gibbs & Barbosa, 2004), and southern Arizona (Alarcon, Davidowitz & Bronstein, 2008). Hawkmoth proboscis length data from Madagascar have also been analysed in relation to the Guanacaste assemblage and were found to be similar (Agosta & Janzen, 2005). Other studies have been limited to particular plant groups, such as orchids (Nilsson et al., 1985, 1987; Nilsson, 1992, 1998; Nilsson, Rabakonandrianina & Pettersson, 1992; Martins & Johnson, 2007). The African flora appears to be particularly rich in moth-pollinated plant taxa (Johnson & Nilsson, 1999; Luyt & Johnson, 2001; Johnson et al., 2003; Anderson, Alexandersson & Johnson, 2010). This is supported by data for African orchids, which show that about 50% of species have floral traits consistent with pollination by moths (Dressler, 1981; Cribb, 1984; Stewart, 1996; Martins & Johnson, 2007). East Africa’s vast seasonal drylands, which include the broader Somali–Maasai regional centre of endemism (Bennun & Njoroge, 1999), have a large number of plant species characterized by white or cream flowers with long narrow corolla tubes, and evening anthesis and scent-production, trait associations that are consistent with pollination by hawkmoths (cf. Baker, 1961; Grant, 1985, 1992; Haber & Frankie, 1989). In this region, genera such as Crinum and Ammocharis (Amaryllidaceae), Carissa (Apocynaceae), Turraea (Meliaceae), Pavetta, Conostomium (Rubiaceae), Cycnium (Orobanchaceae), Jasminium (Oleaceae), and Gladiolus (Iridaceae) all have species with floral traits consistent with hawkmoth pollination. Despite these intriguing patterns, there have been no systematic studies of the occurrence and ecology of interactions between hawkmoths and flowers in a local flora anywhere in Africa. The general aim of this study was to document the ecological interactions between hawkmoths and plants in the seasonally dry tropical ecosystems of Kenya. Specific objectives were (1) to ascertain which plants are utilized as sources of nectar for hawkmoths, (2) to ascertain which hawkmoths are the most frequent flower visitors, (3) to quantify temporal patterns of hawkmoth activity on flowers, (4) to identify specific guilds of plants associated with hawkmoths of varying tongue length, and (5) to quantify patterns of trait covariation that characterize the floral syndrome associated with hawkmoth pollination. MATERIAL AND METHODS STUDY SITES Research for this study was conducted mainly between 2003 and 2005 at two different sites in Kenya, East Africa: Mpala Ranch in Laikipia County and Kitengela in Kajiado County. The Kitengela is a large area of land south of Nairobi National Park encompassing a range of habitats, primarily grassland on ‘black-cotton’ or red laterite soils, with scattered tree bush-savannah and riverine woodland. The specific study sites in this region were in Oloorsirkon Location (01°23.5′S, 036°49.1′E) in Kajiado and a few sites for specific plants within Nairobi National Park (Nairobi County). Altitude is ~1650 m a.s.l. Fieldwork at this site was carried out from late 2003 through the main rainy season, the ‘long rains’ (March–June) in 2004. The second study site, Mpala Ranch (0022.127′N, 036°35.309′E), was located on the plains north of Mt Kenya in northern central Kenya within Laikipia County. Acacia bush-woodland dominates large areas of the red-laterite soils. Rocky outcrops, known as kopjes, of varying size and height are scattered © 2013 The Linnean Society of London, Biological Journal of the Linnean Society, 2013, 110, 199–213 HAWKMOTH POLLINATION IN EAST AFRICA through the area. Altitude is ~1650–2000 m a.s.l. Study sites and plants on Mpala were first assessed during the short rains of 2004 (November) and the main fieldwork was carried out during the long rains of 2005. DIVERSITY AND PHENOLOGY OF PLANTS VISITED BY HAWKMOTHS Detailed field observations were made on focal species that, on the basis of morphological, scent, and temporal characteristics consistent with sphingophily, were hypothesized to be pollinated primarily by hawkmoths (Baker, 1961; Grant, 1985, 1992). These characteristics are long floral tubes, pale coloration, crepuscular/nocturnal scent production, and opening as well as anther dehiscence in the evening or being open primarily in the evening/night. Observations took place sporadically during the day while locating plants and taking measurements, but detailed timed observations were confined to the period from dusk onwards. We did not limit our observations to the focal species and also recorded hawkmoth visits to other plants, including alien species that occur in the same communities. Detailed observations were made on a total of 25 plant species (Table 1). PATTERNS OF HAWKMOTH FORAGING Hawkmoth diversity and foraging patterns were assessed through direct observations at flowers. No attempts were made to quantify pollen loads or the effectiveness of hawkmoths as pollinators. However, in cases where corolla tubes matched or slightly exceeded moth tongue lengths, it was usual to observe large amounts of pollen adhering to the proboscis and body of moths. This was also evident in many of the photographs taken at the study sites (Fig. 1). Hawkmoths were observed directly where there was sufficient light and with additional lighting when needed. After dusk or in the dark, hawkmoths were watched using a dimmed torch (by placing masking tape over the glass) and/or a dimmed headlight. The time of each hawkmoth visit was recorded along with ambient environmental conditions (local weather and cloud cover), number of open flowers on plants, number of flowers visited, and the identity of the visitor. Visitation data were recorded in 1-min intervals. Flowers were watched from c. 18:00 h until about 20–30 min after the last hawkmoth visited at all study sites. Dark-coloured clothing was worn during observations and movements were limited so as not to startle the hawkmoths. The association between floral tube length and the time that hawkmoths spent probing individual flowers was analysed 201 using anaysis of covariance (ANCOVA) with hawkmoth species included as a fixed factor and tube length as a covariate. Light trapping was used to assess the broader patterns of hawkmoth diversity at each site. Due to unsuitable weather conditions and absence of reliable power sources in remote sites, light-trapping was limited and met with varying success. Prior experience with collecting and photography of hawkmoths and other insects in both areas allowed for easy identification of hawkmoths on the wing while feeding at flowers. This was also simplified by the limited number of hawkmoth species to be found foraging from floral resources at both sites. Identifications were based on the collection in the Department of Invertebrate Zoology, National Museums of Kenya, and published catalogues and revisions of the Sphingidae (Pinhey, 1962; Carcasson, 1976; Kitching & Cadiou, 2000). FLORAL MORPHOLOGY, ANTHESIS AND NECTAR Measurements of floral tube lengths of freshly collected flowers were made using a ruler. Anthesis was checked by closely inspecting the anthers, at regular (c. 10 min) intervals from 17:00 h onwards, and lightly brushing them with a paintbrush. Samples of nectar in the study species were taken by carefully detaching individual flowers in the early evening (c. 17:30–18:00 h) before pollinator activity began. Sampling of nectar was done using glass microcapillary tubes (either 5 or100 mL). Nectar was removed from individual flowers by carefully cutting the floral tubes open and drawing the nectar out using capillary action. Nectar sugar concentration was determined using a pocket refractometer (0–50%; Bellingham and Stanley, Turnbridge Wells, UK). ANALYSIS OF TRAIT ASSOCIATIONS The relationships between log-transformed values for corolla tube length and other traits (flower number, nectar volume, nectar concentration) were established using regression of actual values as well as standardized linear phylogenetically independent contrasts (PICs). The latter were calculated using the PDAP module (Midford, Garland & Maddison, 2005) implemented in MESQUITE (Maddison & Maddison, 2006). A phylogeny for the study taxa (Fig. S1) was based on existing published trees and was constructed using PHYLOMATIC (Webb & Donoghue, 2005). Branch lengths were assigned according to Pagel’s arbitrary method (Pagel, 1992), as this resulted in homogenous variance of contrasts, as indicated by the absence of a significant linear relationship between the absolute values of the standardized contrasts and the sum of the squares of branch © 2013 The Linnean Society of London, Biological Journal of the Linnean Society, 2013, 110, 199–213 202 D. J. MARTINS and S. D. JOHNSON Figure 1. Plant habitat and interactions between flowers and hawkmoths: A, Agrius convolvuli visiting flowers of Turraea mombassana; B, Nephele comma inserting its pollen-coated proboscis into the staminal tube of a flower of Turraea mombassana; C, Nephele comma approaching Carissa edulis; D, Nephele comma probing a flower of Grewia bicolor, a diurnal bee-pollinated plant; E, Basiothia medea foraging on Pentanisia ouranogyne, a species whose flowers are also pollinated diurnally by butterflies. F, landscape of Laikipia District, Kenya; G, Agrius convolvuli foraging on flowers of Gynandropsis gynandra. 䉴 lengths (Garland, Harvey & Ives, 1992; Midford et al., 2005). Results of analyses of trait associations are presented only for native plant species. Inclusion of alien plant species in these analyses did not alter the results, but are not presented here as traits of these species would not have evolved through selection by hawkmoths in East Africa. ANALYSIS OF THE KENYAN FLORA The percentage of species in the flora of Kenya that have flowers consistent with pollination by hawkmoths (see above), and the frequency distribution of corolla tube length among these putatively hawkmoth-pollinated species, was calculated. This was done by a thorough analysis of the entire flora of Kenya using published monographs and field guides (Cribb, 1984; Blundell, 1987; Agnew & Agnew, 1994; Beentje, 1994; Stewart, 1996) and measurements of specimens at the East African Herbarium located at the National Museum of Kenya in Nairobi. All known plant species showing traits of sphingophily within the Kenyan flora were included in this analysis. Aspects used in this broad analysis included floral tube/spur length, general morphology and flower colour. RESULTS DIVERSITY AND PHENOLOGY OF PLANTS VISITED BY HAWKMOTHS Hawkmoths were observed to visit the flowers of 25 plant species in 13 different families during the course of this study (Table 1, Supporting Table S1). The duration and patterns of flowering ranged from a few days to several months (Supporting Table S1). Flowering of hawkmoth-visited plants peaked from the end of March/mid-April to August–September in both sites, with a shorter, less intense flowering of some species during the ‘short rains’ in October– November. A number of species, including Jasminium fluminense and Carissa edulis, also flower sporadically at other times of year. PATTERNS OF HAWKMOTH FORAGING We recorded more than 700 bouts of foraging by hawkmoths on the study species. Hawkmoth foraging was observed to take place primarily during a short period of c. 20 min around dusk (Fig. 2). We also observed hawkmoths foraging at dawn on Conostomium quadangulare between 05:00 and 05:15 h at Mpala on 16 September 2004 (N = 14 moths) and on Lantana camara between 05:45 and 05:55 h at Kitengela on 15 August 2005 (N = 21 moths). We did not carry out detailed observations at dawn for the remaining species, but did also observe dawn foraging by an unidentified long-tongued hawkmoth on a Crinum sp. in rainforest habitat in western Kenya. Hawkmoths were observed foraging in all weather conditions, except very heavy rain. As Kenya is an equatorial country, daylength does not change during the year, but the time of sunset shifts by a few minutes during the year, with a corresponding shift in the time of sunrise. Dusk and dawn foraging patterns of hawkmoths loosely follow these shifts (Fig. 2). The mean duration of visits to individual flowers by various hawkmoth species showed a significant positive relationship with flower tube length (F = 11.88, P = 0.04; Fig. 3) and did not vary among species (F = 1.38, P = 0.285) when tube length was taken into account. This relationship remained significant in an analysis that considered only the association between the tube lengths of seven plant species and mean duration of visits by the hawkmoth Agrius convolvuli (F = 6.15, P = 0.048). We recorded between one and six hawkmoth species (mean = 2.58) as visitors to each of the study species (Supporting Table S1). There was a significant nonlinear trend (the best fitted curve was exponential decay) for short-tubed plant species to have a higher diversity of hawkmoth visitors than longer tubed ones (Fig. 4A). Indeed, no more than two hawkmoth species were observed to visit plant species with floral tubes longer than 90 mm. The most common visitor to these long-tubed species was the long-tongued hawkmoth Agrius convolvuli (Supporting Table S1). Plants with flowers of medium depth (20–50 mm) were visited by both long-tongued (Agrius convolvuli) and short/medium-tongued hawkmoths (e.g. Nephele comma, Hippotion celerio, Basiothia medea, and Atemnora westermanii). We made 400 records of foraging bouts by hawkmoths at the Kitengela ecosystem during the main rains in 2004, 100 records during the short rains from Mpala in 2004, 100 records from Borana in February © 2013 The Linnean Society of London, Biological Journal of the Linnean Society, 2013, 110, 199–213 HAWKMOTH POLLINATION IN EAST AFRICA © 2013 The Linnean Society of London, Biological Journal of the Linnean Society, 2013, 110, 199–213 203 204 D. J. MARTINS and S. D. JOHNSON Table 1. Hawkmoth visitors to plant species at the Kitengela and Mpala study sites Hawkmoth species (N) Family Plant species Kitengela Mpala Amaryllidaceae Ammocharis tinneana Crinum macowanii Acokanthera schimperi Carissa edulis Agrius convolvuli (19) Agrius convolvuli (7) Sphingonaepiopsis nana (6) Nephele comma (28) Hippotion celerio (25) Basiothia medea (5) Agrius convolvuli (1) Agrius convolvuli (2) Asteraceae Tithonia diversifolia Euphorbiaceae Croton megalocarpus Nephele comma (3) Basiothia medea (5) Leucostrophus hirundo (5) Cephonodes hylas (4) Macroglossum trochilus (7) Basiothia medea (3) Apocynaceae Croton dichogamus Brassicaceae Maerua decumbens Gynadropsis gynandra Iridaceae Gladiolus ukambanensis Plectranthus pubescens Agrius convolvuli (18) Meliacaea Turraea mombassana Oleaceae Jasminium floribundum Agrius convolvuli (20) Atemnora westermanni (2) Nephele comma (76) Hippotion celerio (5) Basiothia medea (3) Temnora pseudopylas (2) Nephele comma (4) Hippotion celerio (7) Agrius convolvuli (8) Coelonia fulvinotata (3) Agrius convolvuli (17) Coelonia fulvinotata (2) Nephele comma (19) Temnora sp. (2) Hippotion celerio (4) Hippotion celerio (17) Leucostrophus hirundo (2) Jasminium fluminense Orchidaceae Aerangis brachycarpa Rangaeris amaniensis Rubiaceae Pavetta abbyssinica Pentanisia ouranogyne Orobanchaceae Conostomium quadrangulare Cycnium tubulosum Solanaceae Verbenaceae Cycnium ajugifolium Datura stramonium Lantana camara Lippia javanica Hippotion celerio (20) Nephele comma (8) Basiothia medea (6) Agrius convolvuli (22) Nephele comma (25) Hippotion celerio (8) Basiothia medea (14) Temnora pseudopylas (7) Temnora sp. (3) Atemnora westermanii (5) Basiothia medea (4) Agrius convolvuli (2) Nephele comma (7) Nephele comma (85) Hippotion celerio (11) Temnora sp. (2) Basiothia medea (44) Atemnora westermanii (3) Leucostrophus hirundo (4) Basiothia medea (3) Nephele comma (2) Hippotion celerio (3) Nephele comma (10) Hippotion celerio (31) Agrius convolvuli (9) Temnora sp. (2) Basiothia medea (7) Daphnis nerii (6) Hyles sp. (5) Agrius convolvuli (1) Basiothia medea (2) Temnora pseudopylas (3) Agrius convolvuli (1) Nephele comma (4) Hippotion celerio (2) Basiothia medea (8) Nephele comma (11) Hippotion celerio (9) Basiothia medea (12) Hippotion celerio (17) Nephele comma (2) Agrius convolvuli (20) Hippotion celerio (3) Agrius convolvuli (40) © 2013 The Linnean Society of London, Biological Journal of the Linnean Society, 2013, 110, 199–213 HAWKMOTH POLLINATION IN EAST AFRICA 205 A) B) C) D) E) F) G) H) I) J) K) I) M) N) O) P) Q) R) S) Figure 2. Foraging times of hawkmoths observed to visit flowers of dryland plant species in Kenya. Sunset is indicated by the dashed line. See text for details of observations of dawn foraging times. © 2013 The Linnean Society of London, Biological Journal of the Linnean Society, 2013, 110, 199–213 206 D. J. MARTINS and S. D. JOHNSON Foraging time per flower (s) 6 5 4 3 2 1 0 20 40 60 80 100 120 140 160 180 Flower tube length (mm) Figure 3. The relationship between corolla tube length and the mean duration of visits to flowers by hawkmoth species: Agrius convolvuli (䊊), Basiothia medea (䊐), Hippotion celerio (䉮), Nephele comma (䉭). 2005, and 117 records during the long rains at Mpala in 2005. Up to 12 hawkmoth species were recorded at each of the study sites, of which three (Leucostrophus hirundo N = 11, Macroglossum trochilus N = 7, Cephonodes hylas N = 4) are primarily diurnal and are highly generalized foragers. The most commonly encountered hawkmoths with short/medium length tongues were Nephele comma (N = 284), Hippotion celerio (N = 162), Basiothia medea (N = 114), Atemnora westermanii (N = 10), Temnora sp. (N = 9) and Hyles sp. (N = 5). Agrius convolvuli (N = 167) was the most common long-tongued moth observed. There is a sharp discontinuity between the proboscis lengths of A. convolvuli and the other hawkmoths (Table 3). There was a marginally non-significant positive saturating relationship between hawkmoth tongue length and number of plant species visited (Fig. 4B). Agrius convolvuli with the longest tongue (108 mm) and Nephele comma (tongue length = 42 mm) exhibited the highest levels of polyphagy, each having been recorded feeding from flowers of 11 plant species. Number of hawkmoth visitors (A) FLORAL MORPHOLOGY, ANTHESIS AND NECTAR PROPERTIES Tube length (mm) Number of plant species visited (B) Hawkmoth tongue length (mm) Figure 4. A, the relationship between corolla tube length and number of recorded hawkmoth visitors for plants studied in Kenya. B, the relationship between hawkmoth tongue length and number of recorded host nectar plants. Most of the plant species that were visited by hawkmoths have corolla tubes of intermediate length, while a few species have long corolla tubes in excess of 10 cm in length (Table 2). Species with long corolla tubes (> 10 cm) included Crinum macowanii, Ammocharis tinneana, Conostomium quadrangulare, and the two orchids Aerangis brachycarpa and Rangaeris amaniensis. A smaller number of ‘brush’ flowers were also visited by hawkmoths including Maerua decumbens and Gynandropsis gynandra, the latter a species that is also visited by honeybees during the day. The flowers visited by hawkmoths tended to open synchronously before or at dusk. Flowers remained open and available to hawkmoths for varying periods of time from one evening (Conostomium quadrangluare) to 4 weeks (Rangaeris amaniensis). Most of the flowers, other than the two orchid species, remained open for just one and rarely two evenings. All of the flowers that opened in the evenings were still open and available before dawn the next day, but wilted in the hours after sunrise. Scent, where present, was always produced more strongly in the evening (C. quadrangulare, Jasminium spp., P. ouranogyne, A. brachycarpa, R. amaniensis, T. mombassana, C. macowanii, A. tinneana). A few species had no obvious or weak scent (G. gynandra, Cycnium spp.). Nectar volumes in the flowers visited by hawkmoths ranged from 0.47 to 30.5 mL (Table 2). The highest volumes of nectar were found in long-spurred © 2013 The Linnean Society of London, Biological Journal of the Linnean Society, 2013, 110, 199–213 HAWKMOTH POLLINATION IN EAST AFRICA 207 Table 2. Flower corolla length, nectar volumes and nectar concentrations for plants actively visited by hawkmoths at Kitengela and Mpala (N = 10 flowers sampled for each species) Flower tube/spur length (mm) Nectar volume (mL) Species Mean SD Mean SD Mean SD Aerangis brachycarpa Rangaeris amaniensis Conostomium quadrangulare Crinum macowanii Datura stramonium Gladiolus ukambanensis Ammocharis tinneana Gynandropsis gynandra* Cycnium tubulosum Turraea mombassana Jasminium fluminense Maerua decumbens* Pavetta abbysinica Carissa edulis Cycnium ajugifolium Jasminium floribundum Lantana camara Acokanthera schimperi Plectranthus pubescens 158.5 155.8 115.0 105.0 99.6 97.1 84.35 47.6 45.6 43.2 39.7 36.8 28.4 20.3 18.9 18.4 10.1 8.02 6.1 0.44 0.99 0.13 0.45 0.67 0.42 2.82 1.84 6.01 1.62 0.14 2.85 1.25 0.86 1.43 0.71 0.71 0.37 0.7 20.19 9.93 2.6 30.5 8.9 10.7 29.2 0.5 1.55 1.4 0.61 0.88 1.72 0.55 0.51 0.47 0.6 0.43 0.32 2.76 1.18 0.54 9.85 2.24 2.63 6.73 0.18 0.68 0.47 0.21 0.35 0.66 0.21 0.24 0.12 0.17 0.17 0.1 † † 13.9 19.8 21.8 18.4 22.5 48.7 21 21.3 17.8 16.2 18.8 23.1 14.4 13.7 16.8 13.2 18.8 † † 1.58 2.94 2.76 0.67 3.17 3.74 4.38 1.08 2.29 3.35 1.36 2.18 1.82 1.34 3.35 1.70 4.96 Nectar Conc. (%) *No tube, brush type flower, length is that of anthers. †Concentration varies throughout the nectar column (see Martins & Johnson, 2007). orchids (over 20 mL in Aerangis spp. and R. amaniensis) and specialized Amaryllidaceae (c. 30 mL in C. macowanii). ANALYSIS OF TRAIT ASSOCIATIONS Plants with very long corolla tubes tended to produce fewer flowers (Fig. 5A). This relationship was also significant when based on independent contrasts (Fig. 5B). There was a strong positive relationship between corolla tube length and nectar volume, both when using conventional regression (Fig. 5C) as well as independent contrasts (Fig. 5D). Nectar sugar concentrations ranged from 9 to 55% (typically 10–20%, Table 2) and did not show a significant relationship with corolla tube length using either regression based on conventional (P = 0.91) or contrast data (P = 0.16). Sugar content per flower showed a strong positive relationship with corolla tube length in the conventional regression (Fig. 5E), but this relationship was not significant when based on independent contrasts (Fig. 5F). ANALYSIS OF THE KENYAN FLORA A total of 277 species of plants were found to have traits consistent with the floral syndrome of pollina- tion by hawkmoths. This represents about 4% of the total known flora of Kenya (c. 6000 spp.). The distribution of tube/spur lengths among these species is bimodal (Fig. 6), consisting of a large number of species with tubes between 20 and 60 mm, and a small but distinct group of apparently specialized species with tubes/spurs longer than 100 mm. DISCUSSION The results of this study highlight the extraordinarily asymmetric nature of hawkmoth pollination systems. While hawkmoths are clearly polyphagous (Table 1), the plants they visit are often highly specialized (Table 2). Plants adapted for pollination by hawkmoths in Kenya tend to fall into two main guilds. The first guild, consisting of plants with corolla tubes 20–50 mm in length, is visited mainly by a diverse assemblage of hawkmoth species with tongues 30–50 mm in length (Table 3, Fig. 4). The second guild, consisting of plants with corolla tubes > 90 mm in length, is visited almost exclusively by the hawkmoth Agrius convolvuli (Fig. 4) which is the only one of the observed hawkmoths with a tongue long enough to reach nectar in these flowers. Only two long-tongued hawkmoths species frequent the © 2013 The Linnean Society of London, Biological Journal of the Linnean Society, 2013, 110, 199–213 208 D. J. MARTINS and S. D. JOHNSON 1000 (A) 0.4 100 10 1 10 100 0.0 -0.2 -0.4 -0.6 -0.8 0.0 1000 (C) 100 0.4 nectar volume contrasts 10 Nectar volume (ul) Slope = -0.87 R2 = 0.30 P = 0.013 -1.0 1 1 0.1 Slope = 0.94 R2 = 0.70 P < 0.0001 0.01 1 10 100 0.1 0.2 0.3 0.4 0.5 0.6 (D) 0.3 0.2 0.1 Slope = 0.59 R2 = 0.51 P = 0.0005 0.0 -0.1 1000 0.0 (E) 0.3 100 0.1 0.2 0.3 0.4 0.5 0.6 (F) 0.2 sugar content contrasts Sugar content per flower (mg) (B) 0.2 flower number contrasts Number of flowers Slope = -0.82 R2 = 0.48 P = 0.001 10 1 0.1 Slope = 0.44 R2 = 0.47 P = 0.001 0.2 0.2 -0.1 Slope = 0.16 R2 = 0.11 P = 0.17 -0.2 -0.3 0.01 1 10 100 1000 Tube length (mm) 0.0 0.1 0.2 0.3 0.4 0.5 0.6 Positivized tube length contrasts Figure 5. Relationships between flower corolla tube length and other floral traits for native plants visited by hawkmoths in Kenya. Panels on the left are relationships based on actual value. Panels on the right are relationships based on phylogenetically independent contrasts. A, B, tube length; C, D, nectar volume; E, F, sugar content per flower. Figure 6. Bimodal distribution of tube lengths in the sphingophilous flora of Kenya (N = 277 species). drylands of Kenya, and one of these, Coelonia fulvinotata, is restricted to riverine forest habitats with a primarily forest distribution. This means that A. convolvuli is probably responsible for the pollination of almost all of the very long-tubed plants in non-forest habitats in the drylands of Kenya. This ‘Agrius’ guild includes several Crinum species, Ammocharis tinneana, Pancratium tenuifolium, Conostomium quadrangulare, Ipomoea longituba, Ruellia megachlamys, Gladiolus candidus (formerly G. ukambanensis) and Thunbergia guerkheana (Table 1). The effectiveness of Agrius convolvuli as a specialized pollinator in the drylands includes both its ability to disperse widely as well as the abundance of larval host plants (e.g. Ipomoea and Convolvulus spp.) at both sites which in effect can be viewed as ‘subsidising’ the pollination © 2013 The Linnean Society of London, Biological Journal of the Linnean Society, 2013, 110, 199–213 HAWKMOTH POLLINATION IN EAST AFRICA 209 Table 3. Proboscis lengths (mm) of common dryland hawkmoths netted feeding at flowers Male Female Hawkmoth species Mean SD N Mean SD N Agrius convolvuli Hippotion celerio Daphnis nerii Basiothia medea Temnora pseudopylas Nephele comma 108.2 41.2 40.6 22.8 21.7 41.5 6.53 3.63 0.48 0.48 1.16 0.47 14 27 7 11 3 9 96.5 41.5 40 21 22.5 – 0.71 0.71 – – 0.76 – 2 2 1 1 8 – needs of the specialized dryland flora (Feldman, Morris & Wilson, 2004). The discontinuity in proboscis length between the smaller hawkmoths and A. convolvuli and Coelonia fulvinotata may explain why putatively hawkmothpollinated plants in Kenya show a bimodal distribution in corolla tube length (Fig. 6). This result is similar to the bimodal patterns found by Alexandersson & Johnson (2002) and Anderson et al. (2010) in their studies of light-trapped hawkmoth assemblages in South Africa, and Agosta & Janzen (2005) in their study of the Guanacaste assemblage in Costa Rica. The latter study also confirmed that resource overlap by foraging hawkmoths is dependent on tongue length, with long-tongued species able to access nectar resources from short/shorter-tubed flowers but not vice versa. This trend towards greater polyphagy in longer tongued hawkmoths was apparent in our data set, but was marginally nonsignificant (Fig. 4B). Alarcon et al. (2008) suggested that very long-tongued hawkmoths visit flowers of fewer plant species than short-tongued ones, but this was inferred from analysis of pollen load data, which may not be accurate if hawkmoths fail to make contact with anthers of flowers with tubes that are shorter than the proboscis. It is important to note that hawkmoth tongue lengths also reflect phylogenetic patterns (Kawahara et al., 2009) with one clade of larger-bodied moths containing most of the longtonuged species (this group includes Agrius convolvuli, which is the main long-tongued pollinator we observed). Although long-tubed species show apparent specialization for pollination by A. convolvuli, this hawkmoth is highly polyphagous and was recorded as a visitor on many of the plant species with short-tubed flowers (Supporting Table S1). In most instances of foraging on short-tubed species (Fig. 1A, G), A. convolvuli does not make effective contact with anthers and stigmas, and thus probably acts mainly as a nectar robber (see also Johnson, 1995). Contrary to the conventional idea that Lepidoptera are only able to feed effectively on dilute nectar (Kingsolver & Daniel, 1979), A. convolvuli was observed to feed on nectar that ranged in mean sugar concentration from 14% in Conostomium quadrangulare to 47% in Gynandropsis gynandra (Table 2). Hawkmoths with short and medium length tongues fed not only on hawkmoth-adapted flowers, but also on many other species, including bee-pollinated species with very short corollas, such as Grewia bicolor (Fig. 1D). Hawkmoths have been observed to be polyphagous in a number of other studies (Haber & Frankie, 1989; Agosta & Janzen, 2005) covering a range of habitats, visiting both generalized flowers and those adapted for pollination by other animals, such as bats (Baker, 1961, 1963, 1970; Lack, 1978; Baum, 1995; Alarcon et al., 2008) as well as from cultivated garden flowers in Kenya (Ng’weno, 1981) and crops such as coffee and papaya (Martins & Johnson, 2009). Apart from their very long corolla tubes, plants in the A. convolvuli guild tend to have fewer flowers (Fig. 4A, B) and produce more nectar than shortertubed plants (Table 2, Fig. 4C, D). Our interpretation is that because A. convolvuli is highly polyphagous, plants specialized for pollination by this moth are required to produce large volumes of nectar in order to induce fidelity by this insect during its short period of foraging. The trade-off resulting from this investment in floral biomass and nectar is that fewer flowers overall can be maintained. This supports the idea of a flower-size number trade-off (Sargent et al., 2007). It is doubtful that the positive association between flower tube length and nectar volume merely reflects the mechanical constraints on fitting large volumes of nectar into short corolla tubes, as even short-tubed flowers rarely have nectar that fills more than onethird of the corolla tube. Instead, we argue that this association arises because a plant with long-tubed flower that filter out most hawkmoths must entice highly polyphagous hawkmoths with a reward that is much greater than that of sympatric plants with short-tubed flowers that are equally accessible to © 2013 The Linnean Society of London, Biological Journal of the Linnean Society, 2013, 110, 199–213 210 D. J. MARTINS and S. D. JOHNSON these insects. We expect this association to apply to both nectar volume and nectar sugar content. However, the latter association, while also positive, was marginally non-significant when tested using independent contrasts (Fig. 5F). SEASONAL AND TEMPORAL PATTERNS OF HAWKMOTH FORAGING A dozen hawkmoth species, out of a total of c. 100 spp. in Kenya, were regularly recorded on the wing during extensive observations at the study sites (Table 1). In southern Arizona, Alarcon et al. (2008) recorded 14 hawkmoth species in the local fauna, but just three were regularly encountered. In the drylands of Kenya, hawkmoths are constrained by availability and distribution of larval foodplants as well as flowers for the adults to feed from. The seasonal abundance of hawkmoths observed is consistent with data for the region from museum specimens and earlier widespread collecting (Pinhey, 1962; Carcasson, 1976), as well as from other regional studies that focused on collecting hawkmoths (Taylor & Brown, 1972; Robertson, 1977; Kingston & Nummelin, 1998). This pattern is also consistent with studies from other parts of the tropics (Owen, 1969) and the wet–dry seasonal regions of the neotropics where hawkmoths have been studied (Haber & Frankie, 1989; Agosta & Janzen, 2005). The opportunistic feeding behaviour (polyphagy) and rapid dispersal ability of hawkmoths are two factors to consider when interpreting the temporal patterns of hawkmoth foraging. Tropical hawkmoths are large, powerful, long-lived, and also known to mate and lay eggs repeatedly (Pinhey, 1962; Agosta & Janzen, 2005). In the drylands of Kenya, the patchy and unpredictable distribution of many specialized flowers precludes extended foraging constancy. Hawkmoths forage for short specific periods of time (Fig. 2). Observations suggest that nectar resources are rapidly depleted by foraging hawkmoths, especially when large numbers of moths are involved, as is typical on the shrub Carissa edulis and the creeper Jasminium floribundum. This opportunistic feeding was observed to extend to introduced invasive species such as Lantana camara and Tithonia diversifolia (Supporting Table S1), as also observed in Madagascar by Wasserthal (1997). Predation also seems to play a role in the restricted temporal patterns of foraging observed in this study. The major predators of hawkmoths feeding at flowers in the drylands of Kenya were observed to be insectivorous bats (primarily the yellow-winged bat, Lavia frons). These bats catch moths at flowers and as they disperse between patches (D. J. Martins, unpublished data). Bat activity and hawkmoth foraging seem to be closely linked, with two separate peaks, one lagging slightly behind the other at dusk, and probably preceding the other at dawn. We also observed that bats are hunting moths in the middle of the night. If this is widely observed, then predation could be another reason for primarily dusk/after dusk foraging by hawkmoths, as moths have widely been shown to modify their behaviour in relation to bat predation (Lack, 1978; Fenton & Fullard, 1981; Acharya & McNeil, 1998). The observation in this study of a pre-dawn feeding pattern at both sites further reinforces the idea of opportunistic foraging and nectar depletion. This trend has rarely been reported before for tropical hawkmoth pollination studies (Murcia, 1990), but it is probably more widespread. Pre-dawn foraging follows the same patterns as dusk/after dusk, but during this time hawkmoths begin to feed from flowers in the dark before dawn, and foraging ends by the time the sky is light (c. 06:15–06:25 h in Kenya). At both sites, fewer moths foraged at dawn than at dusk, in terms of both abundance and species diversity, indicating that dawn foraging is a ‘second’ lesser peak of activity while dusk foraging remains the main time for feeding from flowers. CONCLUSIONS Interactions between flowers and hawkmoths in Kenya appear to be highly asymmetrical with both short- and long-tongued hawkmoths exhibiting high levels of polyphagy, while flowers, especially longtubed ones, show high levels of specialization. Polyphagous foraging by hawkmoths is of obvious benefit in an environment which is highly seasonal and unpredictable. The high number of East African plants that show apparent specialization for pollination by hawkmoths is likely to reflect the sheer abundance of these insects during certain seasons. Overall, asymmetry in these flower–hawkmoth interactions, especially those involving short-tubed flowers and short-tongued moths, makes it unlikely that they have been shaped by pairwise coevolution (Janzen, 1980; Whittall & Hodges, 2007). Despite the lack of reciprocal specialization, hawkmoths are undoubtedly responsible for the evolution of the long-tubed flowers in this system, and this extends to other components of the African flora, most notably orchids (Martins & Johnson, 2007). The reliance of the specialized sphingophilous dryland flora on a single abundant and widespread hawkmoth species, Agrius convolvuli, is indicative of the importance of long-tongued hawkmoths as ‘keystone pollinator’ species for distinct guilds of flowering plants (Johnson et al., 2004). © 2013 The Linnean Society of London, Biological Journal of the Linnean Society, 2013, 110, 199–213 HAWKMOTH POLLINATION IN EAST AFRICA While our studies documented key aspects of these interactions, such as floral traits, hawkmoth diversity, and foraging patterns, more research is required to establish the extent to which these plants are ecologically dependent on hawkmoths as pollinators. It would also be interesting to determine the effect that invasive plants (many of which are visited by hawkmoths, see Supporting Table S1) are having on native plant species, either as competitors or as facilitators for pollination. ACKNOWLEDGEMENTS We thank the director and staff of the Mpala Research Centre for logistical support and assistance; the Kenya Orchid Society for help with locating orchid populations and loaning plants for experiments and measurements; and the director and staff of the National Museums of Kenya and East African Herbarium for permission to work in their collections. Assistance, useful comments, and logistical support were provided by A. Powys, I. and A. Robertson, H. and R. Campbell, N. Croze, E. Krystall, J. and S. E. Mamlin, P. Kahumbu, N. Georgiadis, M. N. Mutiso, N. E. Pierce, D. Haig, R. and M. Leakey, M. Kinnaird, C. Ngarachu, P. Masinde, A. Kontos and S. Miller. We thank two anonymous reviewers for making very helpful comments that improved the manuscript. This research was supported by a fellowship to D.J.M. from the Smithsonian Institution Women’s Committee and the Mpala Research Centre and by the University of KwaZulu Natal’s School of Life Sciences. REFERENCES Acharya L, McNeil JN. 1998. Predation risk and mating behavior: the responses of moths to bat-like ultrasound. Behavioral Ecology 9: 552–558. Agnew ADQ, Agnew S. 1994. Upland Kenya wild flowers: a flora of the ferns and herbaceous flowering plants of Upland Kenya. Nairobi: East Africa Natural History Society. Agosta SJ, Janzen DH. 2005. Body size distributions of large Costa Rican dry forest moths and the underlying relationship between plant and pollinator morphology. Oikos 108: 183–193. Alarcon R, Davidowitz G, Bronstein JL. 2008. Nectar usage in a southern Arizona hawkmoth community. Ecological Entomology 33: 503–509. Alexandersson R, Johnson SD. 2002. Pollinator-mediated selection on flower-tube length in a hawkmoth-pollinated Gladiolus (Iridaceae). Proceedings of the Royal Society London B 269: 631–636. Anderson B, Alexandersson R, Johnson SD. 2010. Evolution and coexistence of pollination ecotypes in an African Gladiolus (Iridaceae). Evolution 64: 960–972. 211 Baker HG. 1961. The adaptation of flowering plants to nocturnal and crepuscular pollinators. Quarterly Review of Biology 36: 64–73. Baker HG. 1963. Evolutionary mechanisms in pollination biology. Science 139: 877–883. Baker HG. 1970. Two cases of bat pollination in Central America. Revista de Biologia Tropical 17: 187–197. Baum DA. 1995. The comparative pollination and floral biology of baobabs (Adansonia – Bombacaceae). Annals of the Missouri Botanical Garden 82: 322–348. Beentje H. 1994. Kenya trees, shrubs and lianas. Nairobi: National Museums of Kenya. Bennun L, Njoroge P. 1999. Important bird areas in Kenya. Nairobi: The East Africa Natural History Society. Blundell M. 1987. Wildflowers of East Africa. London: William Collins Sons & Co. Ltd. Carcasson RH. 1976. Revised catalogue of the African Sphingidae (Lepidoptera) with descriptions of the East African species. Faringdon, UK: E. W. Classey Ltd.. Cribb P. 1984. Flora of tropical East Africa: Orchidaceae 271. Kew: Royal Botanic Gardens. Cruz-Neto O, Machado IC, Duarte Jr JA, Lopes AV. 2011. Synchronous phenology of hawkmoths (Sphingidae)? and Inga species (Fabaceae–Mimosoideae): implications for the restoration of the Atlantic forest of northeastern Brazil. Biodiversity & Conservation 20: 751–765. Daly KC, Durtschi ML, Smith BH. 2001. Olfactory-based discrimination learning in the moth, Manduca sexta. Journal of Insect Physiology 47: 375–384. Darwin C. 1877. The various contrivances by which orchids are fertilized by insects, 2nd edn. London: John Murray. Dressler RL. 1981. The orchids: natural history and classification. Cambridge, MA: Harvard University Press. Feldman TS, Morris WF, Wilson WG. 2004. When can two plant species facilitate each other’s pollination? Oikos 105: 197–207. Fenton MB, Fullard JH. 1981. Moth hearing and the feeding strategies of bats: variations in the hunting and echolocation behavior of bats may reflect a response to hearing-based defenses evolved by their insect prey. American Scientist 69: 266–275. Garland T, Harvey PH, Ives AR. 1992. Procedures for the analysis of comparative data using phylogenetically independent contrasts. Systematic Biology 41: 18–32. Goyret J, Markwell PM, Raguso RA. 2007. The effect of decoupling olfactory and visual stimuli on the foraging behavior of Manduca sexta. Journal of Experimental Biology 210: 1398–1405. Goyret J, Pfaff M, Raguso RA, Kelber A. 2008. Why do Manduca sexta feed from white flowers? Innate and learnt colour preferences in a hawkmoth. Die Naturwissenschaften 95: 569–576. Goyret J, Raguso RA. 2006. The role of mechanosensory input in flower handling efficiency and learning by Manduca sexta. Journal of Experimental Biology 209: 1585–1593. Grant V. 1985. Additional observations on temperate North American hawkmoth flowers. Botanical Gazette 146: 517– 520. © 2013 The Linnean Society of London, Biological Journal of the Linnean Society, 2013, 110, 199–213 212 D. J. MARTINS and S. D. JOHNSON Grant V. 1992. Floral isolation between ornithophilous and sphingophilous species of Ipomopsis and Aquilegia. Proceedings of the National Academy of Sciences of the United States of America 89: 11828–11831. Haber WA, Frankie GW. 1989. A tropical hawkmoth community: Costa Rican dry forest Sphingidae. Biotropica 21: 155–172. Heinrich B. 1976. Resource partitioning among some eusocial insects: bumblebees. Ecology 57: 874–889. Janzen DH. 1980. When is it coevolution? Evolution 34: 611–612. Johnson SD. 1995. Observations of hawkmoth pollination in the South African orchid Disa cooperi. Nordic Journal of Botany 15: 121–125. Johnson SD, Neal PR, Peter CI, Edwards TJ. 2004. Fruiting failure and limited recruitment in remnant populations of the hawkmoth-pollinated tree Oxyanthus pyriformis subsp pyriformis (Rubiaceae). Biological Conservation 120: 31–39. Johnson SD, Nilsson LA. 1999. Pollen carryover, geitonogamy, and the evolution of deceptive pollination systems in orchids. Ecology 80: 2607–2619. Johnson SD, Peter CI, Ågren J, Nilsson LA. 2003. Pollination success in a deceptive orchid is enhanced by co-occurring rewarding ‘magnet’ plants. Ecology 84: 2919– 2927. Kawahara AY, Mignault AA, Regier JC, Kitching IJ, Mitter C. 2009. Phylogeny and biogeography of hawkmoths (Lepidoptera: Sphingidae): evidence from five nuclear genes. PLoS ONE 4: e5719. Kelber A. 1996. Colour learning in the hawkmoth Macroglossum stellatarum. Journal of Experimental Biology 199: 1127–1131. Kelber A. 1997. Innate preferences for flower features in the hawkmoth Macroglossum stellatarum. Journal of Experimental Biology 200: 827–836. Kelber A, Balkenius A, Warrant EJ. 2002. Scotopic colour vision in nocturnal hawkmoths. Nature 419: 922–925. Kelber A, Pfaff M. 1997. Spontaneous and learned preferences for visual flower features in a diurnal hawkmoth. Israel Journal of Plant Sciences 45: 235–245. Kingsolver JG, Daniel TL. 1979. On the mechanics and energetics of nectar feeding butterflies. Journal of Theoretical Biology. 76: 167–179. Kingston AJ, Nummelin M. 1998. Seasonality and abundance of Sphingids in a garden on the lower slopes of the Uluguru Mountains in Morogoro Township in Tanzania. Journal of East African Natural History 87 (1 & 2): 213– 220. Kitching IJ, Cadiou JM. 2000. Hawkmoths of the world: an annotated and illustrated revisionary checklist. Ithaca and London: The Natural History Museum – Cornell University Press. Lack A. 1978. The ecology of the flowers of the savanna tree Maranthes polyandra and their visitors, with particular reference to bats. Journal of Ecology 66: 287–295. Luyt R, Johnson SD. 2001. Hawkmoth pollination of the African epiphytic orchid Mystacidium venosum, with special reference to flower and pollen longevity. Plant Systematics and Evolution 228: 49–62. Maddison WP, Maddison DR. 2006. Mesquite: a modular system for evolutionary analysis. Version 1.12. Available at: http://mesquiteproject.org Martins DJ, Johnson SD. 2007. Hawkmoth pollination of aerangoid orchids in Kenya, with special reference to nectar sugar gradients in the floral spurs. American Journal of Botany 94: 650–659. Martins DJ, Johnson SD. 2009. Distance and quality of natural habitat influence hawkmoth pollination of cultivated papaya. International Journal of Tropical Insect Science 29: 114–123. Midford PE, Garland JT, Maddison WP. 2005. PDAP package of mesquite. Version 1.07. Miller RB. 1981. Hawkmoths and the geographic patterns of floral variation in Aquilegia caerulea. Evolution 35: 763–774. Miller RB. 1985. Hawkmoth pollination of Aquilegia chrysantha (Ranunculaceae) in Southern Arizona, USA. Southwestern Naturalist 30: 69–76. Miller WE. 1997. Diversity and evolution of tongue length in hawkmoths (Sphingidae). Journal of the Lepidopterists’ Society 51: 9–31. Murcia C. 1990. Effect of floral morphology and temperature on pollen receipt and removal in Ipomoea trichocarpa. Ecology 71: 1098–1109. National Atlas of Kenya. 1969. Kenya Government: survey of Kenya, Nairobi. Ng’weno F. 1981. Hawkmoths in my garden. Bulletin of the East Africa Natural History Society. September – October. Nilsson LA. 1992. Orchid pollination biology. Trends in Ecology and Evolution 7: 255–259. Nilsson LA. 1998. Deep flowers for long tongues. Trends in Ecology and Evolution 13: 259–260. Nilsson LA, Jonsson L, Ralison L, Randrianjohany E. 1987. Angraecoid orchids and hawkmoths in central Madagascar: specialized pollination systems and generalist foragers. Biotropica 19: 310–318. Nilsson LA, Jonsson L, Rason L, Randrianjohany E. 1985. Monophily and pollination mechanisms in Angraecum arachnites Schltr. (Orchidaceae) in a guild of long-tongued hawkmoths (Sphingidae) in Madagascar. Biological Journal of the Linnean Society 26: 1–19. Nilsson LA, Rabakonandrianina E, Pettersson B. 1992. Exact tracking of pollen transfer and mating in plants. Nature 360: 666–667. Oliveira PE, Gibbs PE, Barbosa AA. 2004. Moth pollination of woody species in the cerrados of Central Brazil: a case of so much owed to so few? Plant Systematics & Evolution 245: 41–54. Owen DF. 1969. Species diversity and seasonal abundance in tropical Sphingidae (Lepidoptera). Proceedings of the Royal Entomological Society London A 44: 162–168. Pagel MD. 1992. A method for the analysis of comparative data. Journal of Theoretical Biology 156: 431–442. Papaj DR, Prokopy RJ. 1989. Ecological and evolutionary aspects of learning in phytophagous insects. Annual Review of Entomology 34: 315–350. © 2013 The Linnean Society of London, Biological Journal of the Linnean Society, 2013, 110, 199–213 HAWKMOTH POLLINATION IN EAST AFRICA Pinhey E. 1962. Hawk moths of Central and Southern Africa. South Africa: Longmans, National Museums of Southern Rhodesia. Riffell JA, Alarcon R, Abrell L, Davidowitz G, Bronstein JL, Hildebrand JG. 2008. Behavioral consequences of innate preferences and olfactory learning in hawkmothflower interactions. Proceedings of the National Academy of Sciences of the United States of America 105: 3404– 3409. Robertson IAD. 1977. Records of insects taken at light traps in Tanzania. V – Seasonal changes in catches and effect of the lunar cycle on hawkmoths of subfamily Asemanophorinae (Lepidoptera: Sphingidae). Centre for Overseas Pest Research, Miscellaneous Report No. 31. College House, London. Sargent RD, Goodwillie C, Kalisz S, Rees RH. 2007. Phylogenetic evidence for a flower size and number tradeoff. American Journal of Botany 94: 2059–2062. 213 Stewart J. 1996. Orchids of Kenya. Portland, OR: Timber Press. Taylor LR, Brown ES. 1972. Effects of light-trap design and illumination on samples of moths in the Kenya highlands. Bulletin of Entomological Research 62: 91–112. Wasserthal LT. 1997. The pollinators of the Malagasy star orchids Angraecum sesquipedale, A. sororium and A. compactum and the evolution of extremely long spurs by pollinator shift. Botanica Acta 110: 343–359. Webb CO, Donoghue MJ. 2005. Phylomatic: tree retrieval for applied phylogenetics. Molecular Ecology Notes 5: 181–183. White RH, Stevenson RD, Bennet RR, Cultler DE, Haber WA. 1994. Wavelength discrimination and the role of ultraviolet vision in the feeding behavior of hawkmoths. Biotropica 26: 427–435. Whittall JB, Hodges SA. 2007. Pollinator shifts drive increasingly long nectar spurs in columbine flowers. Nature 447: 706–709. SUPPORTING INFORMATION Additional Supporting Information may be found in the online version of this article at the publisher’s web-site: Figure S1. The phylogeny of plant species visited by hawkmoths that was used for analyses of phylogenetically independent contrasts. Table S1. Phenology and habit of dryland flower species visited by hawkmoths. Habit: T, tree; S, shrub; H, herbaceous; B, bulb (herbaceous); E, epiphyte; Cr, creeper. Distribution: C, common; Sc, scattered clumps/ stands; R, rare. © 2013 The Linnean Society of London, Biological Journal of the Linnean Society, 2013, 110, 199–213
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