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Reproductive Biology |
2Departamento de Zoología, Instituto de Biología, Universidad Nacional Autónoma de México, Apartado Postal 70-153, 04510, Mexico, D. F., Mexico; 3Instituto Manantlán de Ecología y Conservación de la Biodiversidad, Universidad de Guadalajara, Av. Independencia Nacional 151, 48900, Autlán, Jalisco, Mexico
Received for publication April 2, 2004. Accepted for publication November 18, 2004.
ABSTRACT
Flowers of columnar cacti are animal-pollinated, often displaying a chiropterophylic syndrome. This study examined if the columnar cactus Stenocereus queretaroensis, a tropical species endemic to western Mexico, is bat-pollinated, by studying its pollination biology and the foraging behavior of potential pollinators. Flowers were produced in winter through spring, peaking in April. Anthesis was nocturnal, and stigma and anther turgidity began around 2200 hours. Production of nectar secretion and highest sugar concentration and energy supply were nocturnal, peaking between 2200 and 2400 hours. Manual auto-pollination and exclusion experiments showed that self-pollination yielded no fruits, while nocturnal pollinators resulted in high fruit set and seed set compared to diurnal pollination treatments. The nectar-feeding bat Leptonycteris curasoae (Phyllostomidae) was the main nocturnal pollinator with the highest effective pollination. Peak bat visitation coincided with peaks in nectar production. The high abundance of L. curasoae throughout the 4-yr study, suggests that it is a seasonally reliable pollinator for this columnar cactus. While pollination syndromes have been increasingly called into question in recent years, this study suggests that at least for this system, there is a fairly close fit between pollinator and pollination syndrome.
Key Words: Cactaceae columnar cacti Leptonycteris curasoae mutualism nectar-feeding bat pollination ecology Stenocereus queretaroensis west central Mexico
Stebbins (1970)
proposed that the evolution of pollination systems in animal-pollinated plants has been driven by the foraging behavior of the main pollinator, regardless of other pollinator visits to a particular plant. This "most effective pollinator principle" (sensu Stebbins, 1970
) implies selection on floral phenotypes that match morphology of the most effective pollinators. Specialized pollination systems are those that attract a limited subset of potential pollinators, often of a particular taxonomic group (e.g., long-tongued hawkmoths, bees, hummingbirds, bats), and the flowers reflect the size, morphology, and behavioral traits of the pollinators (Baker, 1961
; Faegri and van der Pijl, 1979
). Conversely, empirical evidence suggests that pollination mutualisms often are diversified and opportunistic (Waser et al., 1996
; Olesen and Jordano, 2002
), having different levels of generalization, in part reflecting temporal and spatial fluctuation in the local abundance of pollinators (Waser et al., 1996
). In most plant species, a wide array of taxonomically diverse fauna such as insects, birds, and mammals usually serve as potential pollinators (Ollerton, 1996
; Aigner, 2001
).
Based on flower morphology and nocturnal anthesis, Valiente-Banuet et al. (1996)
proposed that most of the Pachycereae tribe is bat-pollinated, a prediction that has been widely supported (Fleming et al., 1996
; Sahley, 1996
; Nassar et al., 1997
; Valiente-Banuet et al., 1997a
, b
; Casas et al., 1999
; Molina-Freaner et al., 2004
). However, in some of these cactus species, bats are not the exclusive pollinators, and other groups such as some birds or insects can act as the primary pollinators (Alcorn et al., 1959
; McGregor et al., 1962
; Fleming et al., 1996
, 2001
; Sahley, 2001
; Molina-Freaner et al., 2004
). Pollination systems appear to vary along a latitudinal gradient, ranging from tropical specialization to temperate generalization (Olesen and Jordano, 2002
, but see Ollerton and Cranmer, 2002
). Such a pattern has been identified in paniculate agaves, a group of plants that interact with nectar feeding-bats in North America (Arizaga et al., 2000
; Slauson, 2000
; Molina-Freaner and Eguiarte, 2003
). Similarly, chiropterophilic columnar cacti seem to vary latitudinally in their reliance on different pollinators (Valiente-Banuet et al., 1996
; Fleming et al., 2001
). Extratropical chiropterophilic cacti appear to be faced with unpredictable seasonal year-to-year variation in pollinators, and thus plants tend to have a generalist pollination system (Sahley, 1996
, 2001
; Fleming et al., 2001
). Conversely, cacti in tropical regions have a specialized pollination system because of the highly reliable seasonal availability of nectar-feeding bats, thereby leading to a temporally stable pollination system (Petit, 1995
; Nassar et al., 1997
; Valiente-Banuet et al., 1997a
, b
; Casas et al., 1999
).
Two columnar cacti, Stenocereus queretaroensis (Weber) Buxbaum and Pachycereus pecten-aboriginum, coexist in tropical dry forests in the State of Jalisco, in west-central Mexico. Both cacti partially overlap in their reproductive season. Stenocereus queretaroensis and P. pecten-aboriginum have nocturnal anthesis with a chiropterophylic syndrome, although flowers remain open until the afternoon of the following day. Pachycereus pecten-aboriginum did not produce flowers in 2002 and 2003, and S. queretaroensis was the main food source for pollinators during that period (Ibarra-Cerdeña et al., unpublished data). The pollination system in S. queretaroensis appears to be chiropterophylic, although several animals forage on its flowers (CNIC and LIID, personal observations). This apparent paradox of flowers with specialization having a complex community of floral visitors (Ollerton, 1996
) should be resolved by showing that only a small proportion of the visitors' assemblage act as effective pollinators (Johnson and Steiner, 2000
). This has been demonstrated in Calathea ovandensis (Schemske and Horvits, 1984
), where a diverse assemblage of insects visit flowers, but only a small proportion of species acts as effective pollinators.
In this study, we propose that nectar-feeding bats are the main pollinators (sensu Stebbins, 1970
) of S. queretaroensis in Jalisco among a diverse assemblage of potential pollinators in this region. We predicted a strong correlation between nectar production and foraging behavior of nectar-feeding bats. Further, because S. queretaroensis produces flowers every year, this cactus can be considered a reliable food source for the nectar-feeding bat that seasonally visit their populations, and we predicted that bat abundance among years should be constant rather highly variable.
MATERIALS AND METHODS
Study area
This study was conducted in S. queretaroensis stands around the city of Autlán, in the Autlán valley in the state of Jalisco, west central Mexico. This area is located between the 19°42'44'' N and 19°53'52'' N and the 104°14'10'' W and 104°25'38'' W. Elevation is around 900 m a.s.l. Average annual temperature ranges from 20°C to 28°C, and annual precipitation ranges from 600 mm to 1000 mm. Vegetation varies from thorn-scrub and tropical deciduous forest in the valley and lower dry slopes to oak and oak-pine forests at higher altitudes.
Study species
Stenocereus queretaroensis is an arborescent columnar cactus up to heights of 10 m with a short trunk and numerous vertical stems. The cylindrical stems generally have eight prominent ribs and a diameter of 13 to 18 cm. Flowers are 10 to 14 cm long and grow from areolas along the upper half of branches (Pimienta-Barrios and Nobel, 1994
). In the Autlán Valley, this cactus typically reaches sexual maturity at a height of 3 m, with a trunk diameter of 12 cm or a canopy diameter greater than 1.5 m (Benz et al., 1997
). Stenocerus queretaroensis is endemic to western central Mexico and widely distributed in the semiarid regions of Jalisco, Colima, Guanajuato, Michoacan, Queretaro, and Zacatecas (Pimienta-Barrios and Nobel, 1994
).
Floral phenology
Flower phenology was studied by counting all flowers produced by the same 25 mature plants every week during the blooming season in February 2002 and 2003, until no plants were found with buds or flowers, in mid-June. In both years, after the blooming period, we visited the S. queretaroensis stands once a month to check for flowers at other times of the year. Mean flower production per individual was calculated by integrating the area under the phenology curve for the 2002 and 2003 reproductive season.
Floral biology
To characterize the flowers, one flower was collected from 12 individuals and preserved in a solution of formalin, acetic acid, and 70% ethanol (FAA, 5 : 5 : 90 v/v). Floral size was determined by measuring external and internal flower length, perianth width, distance of anthers and stigma to base of floral tube (Nassar et al., 1997
). Hermaphrodite flowers were verified by checking ovules in ovaries and pollen in anthers in this sample. Ovules of each ovary were counted and used for the seed set analysis. The times of anthesis and flower closing were recorded for a randomly chosen flower on each of 10 plants. Flower receptivity was evaluated at the same time by observing anthers and stigma turgidity every hour from opening until closure. Nectar production was measured by removing nectar with a 1-mL gradated syringe every 2 h from one bagged flower per plant (N = 11) from 2000 hours until 0800 hours next morning; this hour was chosen because we sampled some flowers for an entire morning during 2002 and no nectar was produced after that hour (Ibarra-Cerdeña et al., unpublished data). Sugar concentration was quantified using a hand-held refractometer (BRIX30 No 137530LO, Leica, USA) with automatic temperature compensation. Refractometer data were interpreted as sucrose percentage (Dafni, 1992
). Energy supply was calculated as J = 16.8[(S/100) VD], where J is the energy expressed in joules, S is a percentage of sugar reading in the refractometer, V is nectar volume in µL, and D is density of sucrose at the observed concentration (see table 6 in Dafni, 1992
).
Pollination system
To examine self compatibility and contributions of nocturnal and diurnal pollinators in fruit set and seed set, we conducted five treatments for pollination experiments on 130 marked flowers on 75 plants: (1) natural self-pollination (30 flowers of 15 plants)buds were bagged with mosquito netting and left until flower closure; (2) manual self-pollination (30 flowers on 15 plants)buds were bagged and later hand pollinated with their own pollen 2 or 3 h after anthesis (when stigma turgidity was higher), and rebagged until flower closure; (3) nocturnal pollination (20 flowers on 15 plants)flowers were left exposed to pollination visits throughout the night, then bagged just before 0500 hours when nocturnal visitors ceased activity and diurnal pollinators were not yet active; (4) diurnal pollination (20 flowers on 15 plants)buds were bagged during the night with mosquito netting and bags were removed at 0600 hours when no nocturnal pollinators were observed and diurnal pollinators began to forage on flowers; and (5) open pollination (30 flowers on 15 plants)flowers were labeled and left unbagged, and thereby available to both nocturnal and diurnal pollinators. All the experiments were conducted on four consecutive days in 2003, except the manual self-pollination, which was done in 2004. For each of the five treatments, we recorded whether flowers aborted or produced mature fruit. Mature fruits were collected for seed counting 4 wk after the experiments. Because we were not able to recover all fruits from the experiments as a result of harvesting by local people, seed set was analyzed for 17 control fruits and seven fruits each for nocturnal and diurnal pollination treatments. To estimate the efficiency of pollinators, we calculated the seed set (seed produced by fruit/ average number of ovules) for each treatment.
Floral visitors
Diversity, abundance, and activity of night visitors were recorded using a Sony Digital Handy cam DCR-TRV740 with a night-shot feature. The camera was placed 1 to 1.5 m below flowers using a small tripod tied to the stem. This provided a clear shot of the anthers and stigma, plus space to record the entire bat. Videotaping began at sunset before anthesis and continued until 0500 hours because the activity of nocturnal visitors always stops before that hour. For each flower visited, we recorded species, duration of visit, and if visits were legitimate (i.e., visitor's body came in contact with anthers and/or stigma), or illegitimate (no contact with anthers or stigma), regardless of the harvesting of nectar that the visitor can or cannot do. Insects were identified to family and bats to species based on morphological characters and size.
To estimate the abundance of nectar-feeding bats, we captured bats once a week with mist nets in four consecutive years (20002003), using 12 m wide and 3 m high mist nets, which were placed inside and near cacti patches, throughout the cactus reproductive season. In 2000, two mist nets were used, generally open from 0800 to 0200 hours (46 net-h in 4 wk); in 2001, three mist nets were used, generally open from 0800 to 0500 hours (210 net-h in 8 wk); in 2002, three mist nets were open generally from 0800 to 0500 hours (195 net-h in 8 wk); and in 2003, three mist nets were opened generally from 0800 to 0500 hours (170 net-h in 7 wk).
We used binoculars to visually observe diurnal visitors on focal flowers during 9 d in May 2002. Observation lasted for 10 min at 30-min intervals from 0730 until 1040 hours, observing four nearby flowers each day. The total observation time was 360 min (6 h). We recorded the visitor's species, and, in the case of birds, we counted the number of visits. Some insects were collected to identify the species.
Statistical analysis
We performed a goodness of fit analysis to test if frequencies in fruit or abort result in pollination experiments (nocturnal and diurnal pollination) deviated significantly from the control experiment, which was used as the expected frequency. The effect of pollinator exclusion on seed set was analyzed using a Kruskal-Wallis test, with SPSS 10.0 software (SPSS Inc., Chicago, Illinois, USA). Due to the curvilinear response over time of nectar volume, nectar concentration and energy supply, these data sets were analyzed with a second-order polynomial regression (Neter et al., 1996
) using JMP 4.0.2.n (SAS Institute Inc., Cary, North Carolina, USA).
RESULTS
Floral phenology
In 2002, the flowering season began relatively early; when we did the first sample, the average number of flowers per individual was 5.3; the peak occurred in mid-March (11.25 flowers per individual per day) and ended in mid-April. The reproductive season of 2003 began with bud production of S. queretaroensis in early February, although the flowers were present by late February. Flower production peaked in mid-April (4.7 flowers per individual per day) and extended through early June (Fig. 1). Mean of flowers produced in the season by each individual was 322.18 in 2002 and 192.6 in 2003.
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Nectar secretion at anthesis was 0.16 ± 0.04 mL and rapidly peaked at midnight (0.37 ± 0.03 mL) (4 h after anthesis), gradually decreasing until 0800 h when virtually nothing remained (0.03 ± 0.01 mL) (R2 = 0.47, F = 28.03, P < 0.0001, N = 11; Fig. 3a). Sugar concentration was relatively high (20.17 ± 0.5) at anthesis (2000 h), peaking 2 h later (21. 37 ± 0.43) and steadily decreasing towards 0800 hours (9.54 ± 3.04) (R2 = 0.62, F = 51.3, P < 0.0001, N = 11; Fig. 3b). The amount of energy offered by flowers peaked between 2 h and 6 h after anthesis and reached a maximum at 2400 hours (13.90 ± 1.15 J), maintaining maximum energy availability for only 4 h (R2 = 0.47, F = 28.03, P < 0.0001, N = 11; Fig. 3c).
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2 = 1.071, df = 1, P > 0.1), as in the diurnal pollination treatment (
2 = 68.57, df = 1, P < 0.001; Table 1). Statistical differences were observed in seed set between open (mean = 922.88 ± 49.75 SE), nocturnal (mean = 943.57 ± 84.82) and diurnal pollination treatments (mean = 207 ± 58.31) producing less seeds in the last treatment (
2 = 15.78, df = 2, N = 31, P < 0.0005).
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DISCUSSION
The pollination system in S. queretaroensis supports the hypothesis of Valiente-Banuet et al. (1996)
that most Pachycereae cacti are bat-pollinated (but see Fleming et al., 2001
). Flower characteristics such as time of flower opening, stigma receptivity period, and nectar production, support a chiropterophylic syndrome in S. queretaroensis. These traits in floral biology of S. quereretaroensis can be associated with the foraging behavior of L. curasoae, the main pollinator in our study site.
Reproduction by S. queretaroensis occurs only once a year during the dry season. The unimodal pattern of flower production has been described for another locality about 100 km NE of our site (Pimienta-Barrios et al., 2000
). The unimodal pattern has been reported also for columnar cacti in subtropical regions of the Sonoran Desert (Fleming et al., 2001
); however, in the State of Guanajuato, in central México, there are two flowering periods, one coincides with dry season and other with the fall, at the end of the rainy season (Castillo, 2003
).
Cacti grow during the rainy season and stop growing at the beginning of the dry season. Flower display is directly related to the amount of rain in the previous year season (Nobel and Pimienta-Barrios, 1995
). We observed variation between 2 yr at the onset of the flowering season, duration of blooming period, and flower production per plant. In another columnar cacti species at our study site, Pachycereus pecten-aboriginum, the pattern was similar (Ibarra-Cerdeña et al., unpublished data). This suggests that both columnar cacti are responding to the same factors influencing flower production. Fleming et al. (2001)
observed that phenological patterns in cacti of the Sonoran desert are affected by variations in temperature and precipitation. Although these authors predicted that species with specialized pollination systems must produce a relatively constant number of flowers compared with species having a generalist pollination system, neither their data nor ours support this prediction.
Nectar production was unimodal with an abrupt increase and rapid decrease, reaching the maximum of food supply for nocturnal pollinators around midnight (Fig. 2). Bat visits were observed only when cactus flowers had more than 0.86 mL of nectar, suggesting a threshold for visitation by L. curasoae (Horner et al., 1998
). Although most columnar cacti produced high amounts of nectar at night, peaks in nectar quantity and quality varied according to species. Most columnar cacti offer high rewards to pollinators a few hours after anthesis, when nectar-feeding bats are more active (Petit and Freeman, 1997
; Fleming et al., 1996
; Nassar et al., 1997
; Molina-Freaner et al., 2004
). Stenocereus stellatus peaked in nectar production around 0300 hours (Casas et al., 1999
), but the timing of visits of pollinators for this cactus is still unknown. Visit rates estimated in Cardon flowers (Pachycereus pringlei) peaked around 0200 hours, when flowers had more than 0.8 mL of accumulated nectar (Horner et al., 1998
). Given that we did not reinsert nectar, we were unable to determine if nectar removal influenced production, as observed in Stenocereus griseus (increasing nectar secretion) or not, as observed in Subpilocereus repandus (Petit and Freeman, 1997
). Other studies reported no significant or little variation (visits reducing nectar secretion) occurring with simulated visits on nectar production (McDade and Weeks, 2004
).
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Fruit set in S. queretaroensis resulted primarily from nocturnal pollination, with values similar to control treatments (Fig. 3b). Nevertheless, diurnal pollinators also contributed to a substantial proportion of fruit set compared with other tropical species (Nassar et al., 1997
; Valiente-Banuet et al., 1996
, 1997a
, b
, 2004
). It should be noted, however, that their effect on seed production was even lower compared with nocturnal pollinators (Fig. 2); thus nocturnal pollinators were more effective than diurnal at our study site. This might be related to the geographic location, because most tropical columnar cacti depend on nocturnal pollinators, while diurnal or nocturnal pollinators can pollinate subtropical columnar cacti with similar effectiveness (Valiente-Banuet et al., 1996
; Fleming et al., 2001
). Fleming et al. (2001)
argued that the unreliability of L. curasoae in the Sonoran Desert is caused by its virtual absence in spring, when flower and bird densities can be high. Although L. curasoae density in south central Mexico appears similar to the Sonoran Desert, its reliability as a pollinator in these subtropical regions could be greater because (1) flower density is lower compared with the Sonoran desert cacti, resulting in a high fruit set per bat ratio, and (2) bats are present year-round (Rojas-Martinez et al., 1999
).
Visit rates of birds were considerably lower compared with nocturnal visitors. Although flowers remain open until the beginning of the afternoon, the general activity concentrated in the first hours of the morning and decreased in the afternoon, perhaps due to high temperatures and a lack of nectar reward (Fig. 4). We contend that most insects acted as pollen robbers and poor pollinators. Xilocopa sp. was perhaps the only exception because these bumblebees spent less time in each flower and flew longer distances; thus they were potentially legitimate pollinators.
Our study showed that hawkmoths acted as nectar robbers, while L. curasoae was the only nocturnal pollinator. No other bats were recorded as visitors. Although the number of captured individuals of L. curasoae varied in all four years of bat netting, it was always the most frequently captured species, suggesting that this species is a reliable seasonal pollinator for S. queretaroensis, leading to a specialized pollination system (sensu Stebbins, 1970
).
Although pollination syndrome models have been challenged recently, with the argument that generalized pollination systems are more frequent than specialized ones and that plants with specialization are pollinated by a broader than expected range of animals (Wasser et al., 1996
), our study showed a close association between L. curasoae and S. queretaroensis, thus suggesting that the chiropterophilic syndrome is still a useful model. Although we recognize the importance of the diurnal pollinators to support a reasonably high fruit production, their relative importance for seed production (seed set) is considerably low. The consequences of the interaction of nectar-feeding bats and columnar cactus are both proximal, because the number of propagules produced by bat pollination is higher than the production of diurnal pollinators, and ultimately, because bat pollination produced greater genetic variability than other pollinators, as shown by Nassar et al. (2003)
. A remaining challenge is to examine the role of pollinators, seed dispersers, and nurse plants in the population dynamics of the cactus. This has been partially done with the exclusively bat-pollinated cactus Neobuxbamia tetetzo (Godinez-Alvarez et al., 2002
). Future research should include the role of several pollinators and dispersers in the population dynamic of S. queretaroensis.
FOOTNOTES
1 Helpful comments on earlier versions of the manuscript were provided by A. Casas, E. de la Barrera, L. Eguiarte, A. Valiente-Banuet, and E. Yepez. We thank N. Holland and an anonymous reviewer for critical comments that greatly improved the manuscript. I. Cuadriello helped in identifying the insects. We especially thank the Villaseñor family for allowing us to conduct field work on their land, and C. Gómez, P. Ibarra, H. Munguia, H. Orozco, I. Ruan, G. Tinoco, A. Rodríguez, C. Roy, D. Zamora, and D. Villaseñor for assistance in the field and in the lab. The authors wish to thank the Instituto Manantlán de Ecología y Conservación de la Biodiversidad of the Universidad de Guadalajara, and the Instituto de Biología of the Universidad Nacional Autónoma de México for logistical and financial support. This work was partially supported by grants from the North American Bat Conservation Partnership (NABCP) to LIID, and Bat Conservation International (BCI) with a student scholarship fellow to CNIC. The Red Latinoamericana de Botánica awarded CNIC with a graduate scholarship (RLB-03-M1). ![]()
4 Author for reprint requests (liniguez{at}cucsur.udg.mx
) ![]()
LITERATURE CITED
Aigner P. A 2001 Optimality modeling and fitness trade offs: when should plants become pollinator specialists?. Oikos 95: 177-184[CrossRef][ISI]
Alcorn S. M S. E McGregor D. G Butler E. B Kurtz 1959 Pollination requirements of the sahuaro (Carnegia gigantea). Cactus and Succulent Journal 31: 39-41
Arizaga S E Escurra E Peters F Ramírez de Arellano E Vega 2000 Pollination ecology of Agave macroacantha (Agavaceae) in a Mexican tropical desert. II. The role of pollinators. American Journal of Botany 87: 1011-1017
Baker H. G 1961 The adaptations of flowering plants to nocturnal and crepuscular pollinators. Quarterly Review of Biology 36: 64-73[CrossRef]
Benz B F Santana J Cevallos E Muñoz J Rosales M Rosales 1997 The structure and productivity of relict stands of pitaya (Stenocereus queretaroensis; Cactaceae), Jalisco, Mexico. Economic Botany 51: 134-143[ISI]
Casas A A Valiente-Banuet A Rojas-Martinez P Davila 1999 Reproductive biology and the process of domestication of the columnar cactus Stenocereus stellatus in Central Mexico. American Journal of Botany 86: 534-542
Castillo J. P. L 2003 Biología de la polinización de Stenocereus queretaroensis (Weber) Buxbaum, una cactácea con floración biestacional. Undergraduate thesis, Universidad Nacional Autónoma de México, Mexico City, Mexico
Dafni A 1992 Pollination ecology: a practical approach. Oxford University Press, New York, New York, USA
Faegri K L van der Pijl 1979 Principles of pollination ecology. Pergamon Press, Oxford, UK
Fleming T. H M. D Tuttle A. M Horner 1996 Pollination biology and the relative importance of nocturnal and diurnal of nocturnal and diurnal pollinators in three species of Sonoran desert columnar cacti. The Southwestern Naturalist 41: 257-269
Fleming T. H C. T Sahley J. N Holland J. D Nason J. L Hamrick 2001 Sonoran desert columnar cacti and the evolution of generalized pollination systems. Ecological Monograph 71: 511-530
Godinez-Alvarez H A Valiente-Banuet A Rojas-Martinez 2002 The role of seed dispersers in the population dynamics of the columnar cactus Neobuxbaumia tetetzo. Ecology 83: 2617-2629[ISI]
Horner M. A T. H Fleming C. T Sahley 1998 Foraging behaviour and energetics of a nectar-feeding bat, Leptonycteris curasoae (Chiroptera: Phyllostomidae). Journal of Zoological, London 244: 575-586[CrossRef]
Johnson S. D K. E Steiner 2000 Generalization vs. specialization in plant pollinator systems. Trends in Ecology and Evolution 15: 140-143
McDade L. A J. A Weeks 2004 Nectar in hummingbird-pollinated neotropical plants. II. Interactions with flower visitors. Biotropica 36: 216-230[ISI]
McGregor F. S M. A Stanley G Olin 1962 Pollination and pollinating agents of the Saguaro. Ecology 43: 259-267[CrossRef][ISI]
Molina-Freaner F L. E Eguiarte 2003 The pollination biology of two paniculate agaves (Agavaceae) from northwestern Mexico: contrasting roles of bats as pollinators. American Journal of Botany 90: 1016-1024
Molina-Freaner F A Rojas-Martinez T. H Fleming A Valiente-Banuet 2004 Pollination biology of the columnar cactus Pachycereus pecten-aboriginum in north-western Mexico. Journal of Arid Environments 56: 117-127[CrossRef][ISI]
Nassar J. M N Ramirez O Linares 1997 Comparative pollination biology of Venezuelan columnar cacti and the role of nectar-feeding bats in their sexual reproduction. American Journal of Botany 84: 918-927[Abstract]
Nassar J. M J. L Hamrick T. H Fleming 2003 Population genetic structure of Venezuelan chiropterophilous columnar cacti (Cactaceae). American Journal of Botany 90: 1628-1637
Neter J M. H Kutner W Wasserman C. J Nachtsheim 1996 Applied linear regression models, 3rd ed. Richard D. Irwin, Homewood, New Jersey, USA
Nobel P E Pimienta-Barrios 1995 Monthly stem elongation for Stenocereus queretaroensis: relationships to environmental condition, net CO2 uptake and seasonal variations in sugar content. Environmental and Experimental Botany 35: 17-24
Olesen J P Jordano 2002 Geographic patterns in plant pollinator mutualistic networks. Ecology 83: 2416-2424[ISI]
Ollerton J 1996 Reconciling ecological process with phylogenetic patterns: the apparent paradox of plant-pollinator systems. Journal of Ecology 84: 767-769[CrossRef][ISI]
Ollerton J L Cranmer 2002 Latitudinal trends in plant-pollinator interactions: are tropical plants more specialized?. Oikos 98: 340-350[CrossRef][ISI]
Petit S 1995 The pollinators of two species of columnar cacti on Curacao, Netherlands Antilles. Biotropica 27: 538-541[CrossRef][ISI]
Petit S E Freeman 1997 Nectar production of two sympatric species of columnar cacti. Biotropica 29: 175-183[CrossRef][ISI]
Pimienta-Barrios E P Nobel 1994 Pitaya (Stenocereus spp. Cactaceae) an ancient and modern fruit crop of Mexico. Economic Botany 48: 76-83[ISI]
Pimienta-Barrios E J Zañudo E Yépez E Pimienta-Barrios P. S Nobel 2000 Seasonal variation of net CO2 uptake for cactus pear (Opuntia ficus-indica) and pitayo (Stenocereus queretaroensis) in a semi-arid environment. Journal of Arid Environments 44: 73-83[CrossRef][ISI]
Rojas-Martinez A A Valiente-Banuet M. C Arizmendi A Alcantara H Arita 1999 Seasonal distribution of the long-nosed bat (Leptonycteris curasoae) in North America: does a generalized migration pattern really exist?. Journal of Biogeography 26: 1065-1077[CrossRef][ISI]
Sahley C. T 1996 Bat and hummingbird pollination of an autotetraploid columnar cactus, Weberbauerocereus weberbaueri (Cactaceae). American Journal of Botany 83: 1329-1336[CrossRef][ISI]
Sahley C. T 2001 Vertebrate pollination, fruit production, and pollen dispersal of Stenocereus thurberi (Cactaceae). The Southwestern Naturalist 46: 261-271[CrossRef]
Schemske D. W C. C Horvitz 1984 Variation among floral visitors in pollination ability: a precondition for mutualism specialization. Science 225: 519-521
Slauson L. A 2000 Pollination biology of two chiropterophilous Agaves in Arizona. American Journal of Botany 87: 825-836
Stebbins G. L 1970 Adaptative radiation of reproductive characteristics in angiosperms. I. Pollination mechanisms. Annual Review of Ecology and Systematics 1: 307-326
Valiente-Banuet A M. C Arizmendi A Rojas-Martinez L Dominguez-Canseco 1996 Ecological relationships between columnar cacti and nectar-feeding bats in Mexico. Journal of Tropical Ecology 12: 103-119
Valiente-Banuet A A Rojas-Martinez M. C Arizmendi P Davila 1997a Pollination biology of two columnar cacti (Neobuxbaumia mezcalaensis and Neobuxbaumia macrocephala) in the Tehuacan Valley, central Mexico. American Journal of Botany 84: 452-455[Abstract]
Valiente-Banuet A A Rojas-Martinez A Casas M. C Arizmendi P Davila 1997b Pollination biology of two winter-blooming giant columnar cacti in the Tehuacan Valley, central Mexico. Journal of Arid Environments 37: 331-341
Valiente-Banuet A F Molina-Freaner A Torres M. C Arizmendi A Casas 2004 Geographic differentiation in the pollination system of the columnar cactus Pachycereus pecten-aboriginum. American Journal of Botany 91: 850-855
Waser N L Chittka M. V Price N. M Williams J Ollerton 1996 Generalization in pollination systems, and why it matters. Ecology 77: 1043-1060[CrossRef]
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